为满足未来全球粮食需求而增加的氮输入对全球大气N2O收支的潜在影响

Arvin Mosier , Carolien Kroeze
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引用次数: 140

摘要

在大多数土壤中,通过增加硝化和反硝化作用,有效矿质氮的增加促进了N2O的生物成因形成。因此,氮肥直接导致额外的N2O形成。此外,这些输入可能导致N浸出或径流后,或NOx和NH3的气态损失导致NOy和NHx沉积后间接形成N2O。农业系统的人为氮输入包括来自合成肥料、动物粪便、增加的生物固氮、作物残茬返田的矿化以及通过增强有机质矿化来培育有机土壤的氮。氧化亚氮的排放可能是:(1)农田直接排放到大气中,(2)动物圈养或放牧系统排放到大气中,或(3)施用于农业系统的氮通过大气沉降、污水和地表径流输送到地表水和地表水中,最终进入地表水(河流和海洋),在那里产生额外的一氧化二氮。最终,所有通过土壤系统移动的氮要么最终被隔离在土壤中,要么被埋在沉积物中,要么在水生系统中被反硝化。利用联合国粮农组织(FAO)关于肥料投入、作物和动物生产以及人口的数据库和IPCC(1997)估算土壤N2O的方法,我们首先估算了粮食生产中的N投入,然后计算了从1500年到2020年粮食生产系统中N投入产生的N2O排放量。利用这些N2O排放估算值(1990年为~ 6 Tg N, 2020年为~ 9 Tg N)作为一个简单大气箱形模型的输入,我们估算了随时间变化的全球大气N2O浓度。在20世纪,农业用地的快速扩张加上土地利用的集约化可能造成大气N2O净增加的80%左右,从1900年的~ 275 ppbv到1970年的~ 294 ppbv,再到2000年的~ 317 ppbv和2020年的~ 345 ppbv。在未来20年,为了养活额外的15亿人口,需要增加氮肥施用量,因此计算出未来几十年大气中N2O积累的加速速度。这与过去十年观测到的趋势相反,过去十年观测到的趋势表明大气N2O呈线性增加,但与整个20世纪观测到的趋势一致,即大气N2O呈非线性增加。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Potential impact on the global atmospheric N2O budget of the increased nitrogen input required to meet future global food demands

In most soils, biogenic formation of N2O is enhanced by an increase in available mineral N through increased nitrification and denitrification. N-fertilization, therefore, directly results in additional N2O formation. In addition, these inputs may lead to indirect formation of N2O after N leaching or runoff, or following deposition of NOy and NHx from gaseous losses of NOx and NH3. Anthropogenic N input into agricultural systems includes N from synthetic fertilizer, animal wastes, increased biological N-fixation, mineralization of crop residue returned to the field and cultivation of organic soils through enhanced organic matter mineralization. Nitrous oxide may be emitted (1) directly to the atmosphere from agricultural fields, (2) from animal confinements or pastoral systems, or (3) from N applied to agricultural systems which is transported into ground and surface waters through atmospheric deposition, sewage and surface runoff and eventually into surface water (rivers and oceans) where additional N2O is produced. Eventually, all N that moves through the soil system will be either terminally sequestered in soil or buried sediments or denitrified in aquatic systems.

Using Food and Agricultural Organization of the United Nations (FAO) databases for fertilizer input, crop and animal production, and human population and the IPCC (1997) methodology for estimating N2O from soil, we first estimated the N input into food production and then calculated N2O emissions derived from N input into food production systems from 1500 until the year 2020. Using these estimates for N2O emissions (∼6 Tg N in 1990 and ∼9 Tg N in 2020) as input to a simple atmospheric box model we estimated global atmospheric N2O concentrations over time. During the 20th century, a fast expansion of agricultural land coupled with intensification of land use probably caused about 80% of the net increase in atmospheric N2O, from ∼275 ppbv in 1900 to ∼294 ppbv in 1970, to projected concentrations of ∼317 in 2000 and ∼345 in 2020. With the increasing amount of fertilizer N application needed to feed an additional 1.5 billion people in the next 20 years, an accelerated rate of N2O accumulation in the atmosphere is calculated for the coming decades. This is in contrast with the observed trends during the past decade, which indicate a linear increase in atmospheric N2O, but is in line with observed trends during the whole 20th century, which show a non-linear increase in atmospheric N2O.

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