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利用稳定同位素和水化学耦联评估水文和生物地球化学过程对河流氮源的作用。

Coupling stable isotopes and water chemistry to assess the role of hydrological and biogeochemical processes on riverine nitrogen sources.

机构信息

College of Environmental & Resource Sciences, Zhejiang University, Hangzhou, 310058, China; Zhejiang Provincial Key Laboratory of Subtropical Soil and Plant Nutrition, Zhejiang University, Hangzhou, 310058, China.

College of Environmental & Resource Sciences, Zhejiang University, Hangzhou, 310058, China.

出版信息

Water Res. 2019 Mar 1;150:418-430. doi: 10.1016/j.watres.2018.11.082. Epub 2018 Dec 6.

Abstract

Accurate source identification is critical for optimizing water pollution control strategies. Although the dual stable isotope (N-NO/O-NO) approach has been widely applied for differentiating riverine nitrogen (N) sources, the relatively short-term (<1 yr) N-NO/O-NO records typically used in previous studies often hinders rigorous assessment due to high temporal variability associated with watershed N dynamics. Estimated contributions of legacy N sources in soils and groundwater to riverine N export by modeling approaches in many previous studies also lack validation from complementary information, such as multiple stable isotopes. This study integrated three years of multiple stable isotope (N-NO/O-NO and H-HO/O-HO) and hydrochemistry measurements for river water, groundwater and rainfall to elucidate N dynamics and sources in the Yongan watershed (2474 km) of eastern China. Nonpoint source N pollution dominated and displayed considerable seasonal and spatial variability in N forms and concentrations. Information from δN-NO and δO-NO indicated that riverine N dynamics were regulated by contributing sources, nitrification and denitrification, as well as hydrological processes. For the three examined catchments and entire watershed, slow subsurface and groundwater flows accounted for >75% of river discharge and were likely the major hydrological pathways for N delivery to the river. Riverine NO sources varied with dominant land use (p < 0.001), with the highest contributions of groundwater (60%), wastewater (35%), and soil (50%) occurring in agricultural, residential and forest catchments, respectively. For the entire watershed, groundwater (∼50%) and soil N (>30%) were the dominant riverine NO sources, implying considerable potential for N pollution legacy effects. Results were consistent with observed nitrous oxide dynamics and N sources identified in previous modeling studies. As the first attempt to apply multiple isotope tracers for exploring and quantifying N transformation and transport pathways, this study provides an integrated approach for verifying and understanding the N pollution legacy effects observed in many watersheds worldwide. This study highlights that river N pollution control in many watersheds requires particular attention to groundwater restoration and soil N management in addition to N input control strategies.

摘要

准确的源识别对于优化水污染控制策略至关重要。尽管双稳定同位素(N-NO/O-NO)方法已被广泛应用于区分河流氮(N)源,但以前研究中常用的相对短期(<1 年)的 N-NO/O-NO 记录由于与流域 N 动态相关的高度时间变异性,通常会阻碍严格评估。许多先前研究中的建模方法估计土壤和地下水中遗留 N 源对河流 N 输出的贡献也缺乏来自互补信息(如多种稳定同位素)的验证。本研究整合了三年的多个稳定同位素(N-NO/O-NO 和 H-HO/O-HO)和水文化学测量,以阐明中国东部永安流域(2474km)的 N 动态和来源。非点源 N 污染占主导地位,N 形态和浓度表现出相当大的季节性和空间变异性。δN-NO 和 δO-NO 的信息表明,河流 N 动态受贡献源、硝化和反硝化以及水文过程的调节。对于三个检查流域和整个流域,缓慢的地下和地下水流动占河流流量的>75%,并且可能是 N 输送到河流的主要水文途径。河流 NO 源随主要土地利用而变化(p<0.001),农业、住宅和森林流域中地下水(60%)、废水(35%)和土壤(50%)的贡献最高。对于整个流域,地下水(约 50%)和土壤 N(>30%)是河流 NO 的主要来源,这意味着 N 污染遗留效应的潜力相当大。结果与先前建模研究中观察到的氧化亚氮动态和 N 源一致。作为首次应用多种同位素示踪剂探索和量化 N 转化和输运途径的尝试,本研究提供了一种综合方法,用于验证和理解全球许多流域观察到的 N 污染遗留效应。本研究强调,除了氮输入控制策略外,许多流域的河流 N 污染控制还需要特别关注地下水恢复和土壤 N 管理。

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