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运用空间明确方法,使中国的氮气使用保持在行星边界内。

Keeping Nitrogen Use in China within the Planetary Boundary Using a Spatially Explicit Approach.

机构信息

Key Laboratory of Agricultural Water Resources, Hebei Key Laboratory of Soil Ecology, Center for Agricultural Resources Research, Institute of Genetics and Developmental Biology, Chinese Academy of Sciences, 286 Huaizhong Road, Shijiazhuang 050021, China.

Water Systems and Global Change Group, Wageningen University & Research, Droevendaalsesteeg 4, 6708 PB Wageningen, The Netherlands.

出版信息

Environ Sci Technol. 2024 Jun 4;58(22):9689-9700. doi: 10.1021/acs.est.4c00908. Epub 2024 May 23.

DOI:10.1021/acs.est.4c00908
PMID:38780255
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC11155250/
Abstract

Nitrogen (N) supports food production, but its excess causes water pollution. We lack an understanding of the boundary of N for water quality while considering complex relationships between N inputs and in-stream N concentrations. Our knowledge is limited to regional reduction targets to secure food production. Here, we aim to derive a spatially explicit boundary of N inputs to rivers for surface water quality using a bottom-up approach and to explore ways to meet the derived N boundary while considering the associated impacts on both surface water quality and food production in China. We modified a multiscale nutrient modeling system simulating around 6.5 Tg of N inputs to rivers that are allowed for whole of China in 2012. Maximum allowed N inputs to rivers are higher for intensive food production regions and lower for highly urbanized regions. When fertilizer and manure use is reduced, 45-76% of the streams could meet the N water quality threshold under different scenarios. A comparison of "water quality first" and "food production first" scenarios indicates that trade-offs between water quality and food production exist in 2-8% of the streams, which may put 7-28% of crop production at stake. Our insights could support region-specific policies for improving water quality.

摘要

氮(N)支持粮食生产,但过量会导致水污染。在考虑氮输入与河流中氮浓度之间复杂关系的同时,我们缺乏对水质氮边界的理解。我们的知识仅限于确保粮食生产的区域减排目标。在这里,我们旨在使用自下而上的方法,从空间上确定河流中氮输入的边界,以确保地表水质量,并探索在考虑对中国地表水质量和粮食生产的相关影响的情况下,满足所推导的氮边界的方法。我们修改了一个多尺度养分模型系统,模拟了 2012 年中国整个地区允许的约 6.5 亿吨氮输入到河流中。对于集约化粮食生产地区,允许进入河流的最大氮输入较高,而对于高度城市化地区,允许进入河流的最大氮输入较低。当减少化肥和粪肥使用时,在不同情景下,有 45-76%的溪流可以达到氮水质阈值。“水质优先”和“粮食生产优先”情景的比较表明,在 2-8%的溪流中存在水质和粮食生产之间的权衡,这可能使 7-28%的作物生产受到威胁。我们的观点可以为改善水质的区域特定政策提供支持。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3114/11155250/7945c557f89a/es4c00908_0006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3114/11155250/099676ad8e61/es4c00908_0001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3114/11155250/c7089c271c2f/es4c00908_0002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3114/11155250/70596435793e/es4c00908_0003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3114/11155250/e9c14d3d6d35/es4c00908_0004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3114/11155250/ab52125461da/es4c00908_0005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3114/11155250/7945c557f89a/es4c00908_0006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3114/11155250/099676ad8e61/es4c00908_0001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3114/11155250/c7089c271c2f/es4c00908_0002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3114/11155250/70596435793e/es4c00908_0003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3114/11155250/e9c14d3d6d35/es4c00908_0004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3114/11155250/ab52125461da/es4c00908_0005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/3114/11155250/7945c557f89a/es4c00908_0006.jpg

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本文引用的文献

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Food production in China requires intensified measures to be consistent with national and provincial environmental boundaries.中国的粮食生产需要采取强化措施,以符合国家和省级的环境界限。
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[Research basis of ecological thresholds and regime shifts in China].[中国生态阈值与 regime shifts 的研究基础] 注:“regime shifts”直接保留英文,可能是特定的专业术语未找到准确对应的中文表述,在医学专业文献中这种情况较常见。
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