Department of Plant Ecology, Justus-Liebig-University Giessen, Giessen, Germany.
Department of Biogeochemistry, Max Planck Institute for Terrestrial Microbiology, Marburg, Germany.
Glob Chang Biol. 2018 Sep;24(9):3897-3910. doi: 10.1111/gcb.14136. Epub 2018 Apr 16.
Rising atmospheric CO concentrations are expected to increase nitrous oxide (N O) emissions from soils via changes in microbial nitrogen (N) transformations. Several studies have shown that N O emission increases under elevated atmospheric CO (eCO ), but the underlying processes are not yet fully understood. Here, we present results showing changes in soil N transformation dynamics from the Giessen Free Air CO Enrichment (GiFACE): a permanent grassland that has been exposed to eCO , +20% relative to ambient concentrations (aCO ), for 15 years. We applied in the field an ammonium-nitrate fertilizer solution, in which either ammonium ( ) or nitrate ( ) was labelled with N. The simultaneous gross N transformation rates were analysed with a N tracing model and a solver method. The results confirmed that after 15 years of eCO the N O emissions under eCO were still more than twofold higher than under aCO . The tracing model results indicated that plant uptake of did not differ between treatments, but uptake of was significantly reduced under eCO . However, the and availability increased slightly under eCO . The N O isotopic signature indicated that under eCO the sources of the additional emissions, 8,407 μg N O-N/m during the first 58 days after labelling, were associated with reduction (+2.0%), oxidation (+11.1%) and organic N oxidation (+86.9%). We presume that increased plant growth and root exudation under eCO provided an additional source of bioavailable supply of energy that triggered as a priming effect the stimulation of microbial soil organic matter (SOM) mineralization and fostered the activity of the bacterial nitrite reductase. The resulting increase in incomplete denitrification and therefore an increased N O:N emission ratio, explains the doubling of N O emissions. If this occurs over a wide area of grasslands in the future, this positive feedback reaction may significantly accelerate climate change.
大气中 CO 浓度的升高预计将通过改变微生物氮(N)转化来增加土壤中的氧化亚氮(N O)排放。几项研究表明,在大气 CO 升高(eCO )下,N O 排放量增加,但背后的过程尚不完全清楚。在这里,我们展示了吉森自由空气 CO 增浓(GiFACE)的结果:一个永久草地已经暴露在 eCO 下,相对于环境浓度(aCO )增加了 20%,已经 15 年了。我们在田间应用了一种铵-硝酸盐肥料溶液,其中铵( )或硝酸盐( )用 N 标记。同时,使用 N 示踪模型和求解器方法分析了总氮转化速率。结果证实,在 eCO 15 年后,eCO 下的 N O 排放量仍高于 aCO 下的两倍以上。示踪模型的结果表明,处理之间植物对 的吸收没有差异,但在 eCO 下, 吸收明显减少。然而,eCO 下的 和 可用性略有增加。N O 同位素特征表明,在 eCO 下,额外排放的源,在标记后前 58 天内为 8407μg N O-N/m,与 还原(+2.0%)、 氧化(+11.1%)和有机 N 氧化(+86.9%)有关。我们推测,eCO 下植物生长和根渗出物的增加提供了额外的生物可利用能源供应源,这作为一种激发效应触发了微生物土壤有机质(SOM)矿化的刺激,并促进了亚硝酸盐还原酶的活性。不完全反硝化的增加以及因此 N O:N 排放比的增加,解释了 N O 排放的增加。如果未来在大面积的草原上发生这种情况,这种正反馈反应可能会显著加速气候变化。