Yu Lu, Zheng Tianyuan, Yuan Ruyu, Zheng Xilai
College of Environmental Science and Engineering, Ocean University of China, Qingdao, 266100, China; Ecological Environment Research and Development Center, Weihai Innovation Institute, Qingdao University, Weihai, 264200, China.
College of Environmental Science and Engineering, Ocean University of China, Qingdao, 266100, China; Key Lab of Marine Environmental Science and Ecology, Ministry of Education, Ocean University of China, Qingdao, 266100, China.
J Environ Manage. 2022 Jul 15;314:115101. doi: 10.1016/j.jenvman.2022.115101. Epub 2022 Apr 23.
Nitrate (NO) contamination in groundwater has diverse sources and complicated transformation processes. To effectively control NO pollution in groundwater systems, quantitative and accurate identification of NO sources is critical. In this work, we applied hydrochemical characteristics and isotope analysis to determine NO source apportionment. For the first time, the NO source contributions were calculated using hydrochemical indicators combined with multivariate statistical model (PCA-APCS-MLR). The results interpret that chemical fertilizers (58.11%) and natural sources (22.69%) were the primary NO sources in the vegetable cultivation area (VCA) which were rather close to the estimation by Bayesian isotope mixing model (SIAR). In particular, the contributions of chemical fertilizers in the VCA differed by only 3.79% between the two methods. Compared with previous approaches e.g. SIAR, the key advantage of the proposed PCA-APCS-MLR model is that it only requires the hydrochemical indicators which can be easily measured. A series of complicated experiments including measurement of isotope data of NO in groundwater, monitoring of in-situ pollution source information and calculation of isotopic enrichment factor can be simply avoided. The PCA-APCS-MLR model offers a much more convenient and faster method to determine the contribution rates of NO pollution sources in groundwater.
地下水中硝酸盐(NO)污染来源多样,转化过程复杂。为有效控制地下水系统中的NO污染,定量准确识别NO来源至关重要。在本研究中,我们应用水化学特征和同位素分析来确定NO源的分配。首次使用水化学指标结合多元统计模型(PCA-APCS-MLR)计算NO源贡献率。结果表明,化肥(58.11%)和自然源(22.69%)是蔬菜种植区(VCA)的主要NO来源,这与贝叶斯同位素混合模型(SIAR)的估计结果相当接近。特别是,两种方法计算出的VCA中化肥贡献率仅相差3.79%。与以往方法(如SIAR)相比,所提出的PCA-APCS-MLR模型的关键优势在于它只需要易于测量的水化学指标。可以避免一系列复杂的实验,包括测量地下水中NO的同位素数据、监测原位污染源信息以及计算同位素富集因子。PCA-APCS-MLR模型为确定地下水中NO污染源贡献率提供了一种更便捷、快速的方法。