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1
Biological nitrogen fixation: rates, patterns and ecological controls in terrestrial ecosystems.生物固氮:陆地生态系统中的速率、模式和生态控制。
Philos Trans R Soc Lond B Biol Sci. 2013 May 27;368(1621):20130119. doi: 10.1098/rstb.2013.0119. Print 2013 Jul 5.
2
Global trends and uncertainties in terrestrial denitrification and N₂O emissions.全球陆地反硝化和 N₂O 排放的趋势和不确定性。
Philos Trans R Soc Lond B Biol Sci. 2013 May 27;368(1621):20130112. doi: 10.1098/rstb.2013.0112. Print 2013 Jul 5.
3
Closing yield gaps through nutrient and water management.通过养分和水分管理来缩小产量差距。
Nature. 2012 Oct 11;490(7419):254-7. doi: 10.1038/nature11420. Epub 2012 Aug 29.
4
Restoration of ponds in rural landscapes: modelling the effect on nitrate contamination of surface water (the Seine River Basin, France).农村景观池塘的修复:模拟对地表水硝酸盐污染的影响(法国塞纳河流域)。
Sci Total Environ. 2012 Jul 15;430:280-90. doi: 10.1016/j.scitotenv.2012.04.035. Epub 2012 Jun 8.
5
Comparing the yields of organic and conventional agriculture.比较有机农业和常规农业的产量。
Nature. 2012 May 10;485(7397):229-32. doi: 10.1038/nature11069.
6
Global food demand and the sustainable intensification of agriculture.全球粮食需求与农业可持续集约化发展。
Proc Natl Acad Sci U S A. 2011 Dec 13;108(50):20260-4. doi: 10.1073/pnas.1116437108. Epub 2011 Nov 21.
7
Solutions for a cultivated planet.为培育的星球寻找解决方案。
Nature. 2011 Oct 12;478(7369):337-42. doi: 10.1038/nature10452.
8
Long term change of nutrient concentrations of rivers discharging in European seas.河流向欧洲海域排放的营养物浓度的长期变化。
Sci Total Environ. 2011 Nov 1;409(23):4899-916. doi: 10.1016/j.scitotenv.2011.08.015. Epub 2011 Sep 10.
9
Fertilizing nature: a tragedy of excess in the commons.《养育自然:公地的过度悲剧》
PLoS Biol. 2011 Aug;9(8):e1001124. doi: 10.1371/journal.pbio.1001124. Epub 2011 Aug 16.
10
Exploring global changes in nitrogen and phosphorus cycles in agriculture induced by livestock production over the 1900-2050 period.探究 1900-2050 年期间由畜牧业生产引起的农业氮磷循环的全球变化。
Proc Natl Acad Sci U S A. 2013 Dec 24;110(52):20882-7. doi: 10.1073/pnas.1012878108. Epub 2011 May 16.

氮在农业土壤与海洋之间的级联过程:区域流域和全球尺度上氮迁移的模拟。

The nitrogen cascade from agricultural soils to the sea: modelling nitrogen transfers at regional watershed and global scales.

机构信息

UMR Sisyphe, CNRS/University P. & M. Curie, 4 place Jussieu, Paris 75005, France.

出版信息

Philos Trans R Soc Lond B Biol Sci. 2013 May 27;368(1621):20130123. doi: 10.1098/rstb.2013.0123. Print 2013 Jul 5.

DOI:10.1098/rstb.2013.0123
PMID:23713121
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC3682743/
Abstract

The nitrogen cycle of pre-industrial ecosystems has long been remarkably closed, in spite of the high mobility of this element in the atmosphere and hydrosphere. Inter-regional and international commercial exchanges of agricultural goods, which considerably increased after the generalization of the use of synthetic nitrogen fertilizers, introduced an additional type of nitrogen mobility, which nowadays rivals the atmospheric and hydrological fluxes in intensity, and causes their enhancement at the local, regional and global scales. Eighty-five per cent of the net anthropogenic input of reactive nitrogen occurs on only 43 per cent of the land area. Modern agriculture based on the use of synthetic fertilizers and the decoupling of crop and animal production is responsible for the largest part of anthropogenic losses of reactive nitrogen to the environment. In terms of levers for better managing the nitrogen cascade, beyond technical improvement of agricultural practices tending to increase nitrogen use efficiency, or environmental engineering management measures to increase nitrogen sinks in the landscape, the need to better localize crop production and livestock breeding, on the one hand, and agriculture and food demand on the other hand, is put forward as a condition to being able to supply food to human populations while preserving environmental resources.

摘要

尽管氮元素在大气圈和水圈中具有很高的流动性,但工业化前生态系统的氮循环长期以来一直非常封闭。在合成氮肥广泛使用之后,农产品的区域间和国际商业交流大大增加,引入了一种额外的氮流动类型,这种流动类型如今在强度上可与大气和水文通量相媲美,并导致它们在局部、区域和全球范围内增强。只有 43%的陆地面积承载了 85%的人为活性氮净输入。基于使用合成肥料和作物与动物生产脱钩的现代农业,是导致人为活性氮向环境中大量流失的主要原因。在更好地管理氮级联的手段方面,除了提高农业实践以提高氮利用效率的技术改进,或增加景观中氮汇的环境工程管理措施外,一方面需要更好地本地化作物生产和牲畜养殖,另一方面需要本地化农业和粮食需求,这是在保护环境资源的同时为人类提供食物的条件。