Zhao Qiang, Lü Cheng-Wen, Qin Xiao-Bo, Wu Hong-Bao, Wan Yun-Fan, Liao Yu-Lin, Lu Yan-Hong, Li Jian-Ling
Key Laboratory of Agricultural Environment, Ministry of Agriculture, Institute of Environment and Sustainable Development in Agriculture, Chinese Academy of Agricultural Sciences, Beijing 100081, China.
College of Territorial Resources and Tourism, Anhui Normal University, Wuhu 241000, China.
Huan Jing Ke Xue. 2018 Oct 8;39(10):4497-4504. doi: 10.13227/j.hjkx.201802026.
The nitrogen (N) pollution of water is a common global problem. To understand the key production process of N O and identify the dominant N sources, Tuojia River, a typical agricultural watershed in a subtropical area, was investigated. To analyze the characteristics of dual nitrate isotopes (δN-NO,δO-NO) in water, and N isotope (δN) and carbon-nitrogen ratio (C/N) in sediment organic matter from four reaches(S1-S4), the stable isotopes method was used. The results showed that the sources of nitrate varied significantly among river segments and were affected by agricultural production and human habitation on the land surface. The average δN-NO in reaches S1, S2, S3, and S4 were 1.72‰, 2.62‰, 4.10‰, and -1.28‰, respectively, while the average δO-NO were 2.60‰,-0.06‰, 0.85‰, and -0.62‰. The N in terrestrial soil made a large contribution to nitrate sources in reach S1, while soil N, ammonium N fertilizer, and manure played a main role in reaches S2 and S3. Most of the nitrate came from ammonium N fertilizer in reach S4. We also found that δN in sediment organic matter ranged from -0.69‰ to 11.21‰, and C/N was between 7.30 and 12.02. The mean δN in reaches S1-S4 were 1.91‰, 2.96‰, 4.72‰, and 3.23‰, respectively, and the mean C/N values were 10.62, 8.63, 9.05, and 9.22, respectively. Although there were some differences in δN among reaches S2-S4, the dominant N source was sewage in those reaches. However, soil organic matter was the main N source in the sediments of reach S1. The mean δO-NO in reaches S1-S4 were -7.01‰,-0.17‰,-0.28‰, and -0.60‰, respectively, indicating that nitrification was the key N O production process in these reaches. The ratios of δN-NO and δO-NO were 0.66,-41.01,-30.23, and 9.39 in reaches S1-S4, respectively. Finally, we found that there was a positive correlation between NO-N and δN-NO. To summarize, the N transformation and N O production could be dominated by the nitrification process in Tuojia River.
水体氮污染是一个全球性的普遍问题。为了解NO的关键产生过程并确定主要氮源,对亚热带地区典型农业流域——驮家河进行了调查。为分析四个河段(S1 - S4)水体中双硝酸盐同位素(δN - NO、δO - NO)以及沉积物有机质中氮同位素(δN)和碳氮比(C/N)的特征,采用了稳定同位素方法。结果表明,各河段硝酸盐来源差异显著,受地表农业生产和人类居住活动影响。S1、S2、S3和S4河段的平均δN - NO分别为1.72‰、2.62‰、4.10‰和 - 1.28‰,而平均δO - NO分别为2.60‰、 - 0.06‰、0.85‰和 - 0.62‰。陆地土壤中的氮对S1河段硝酸盐来源贡献较大,而土壤氮、铵态氮肥和粪肥在S2和S3河段起主要作用。S4河段的硝酸盐大多来自铵态氮肥。我们还发现沉积物有机质中的δN范围为 - 0.69‰至11.21‰,C/N在7.30至12.02之间。S1 - S4河段的平均δN分别为1.91‰、2.96‰、4.72‰和3.23‰,平均C/N值分别为10.62、8.63、9.05和9.22。尽管S2 - S4河段的δN存在一些差异,但这些河段的主要氮源是污水。然而,S1河段沉积物中的主要氮源是土壤有机质。S1 - S4河段的平均δO - NO分别为 - 7.01‰、 - 0.17‰、 - 0.28‰和 - 0.60‰,表明硝化作用是这些河段NO的关键产生过程。S1 - S4河段的δN - NO与δO - NO比值分别为0.66、 - 41.01、 - 30.23和9.39。最后,我们发现NO - N与δN - NO之间存在正相关关系。综上所述,驮家河的氮转化和NO产生可能以硝化过程为主导。