自行车
环境科学
生态系统
硝化作用
氮气循环
农学
盐度
土壤盐分
铵
氮气
硝酸盐
环境化学
土壤水分
土壤pH值
作物产量
反硝化
浸出(土壤学)
浸出模型
土壤有机质
生产力
固氮
土壤质量
旱地盐分
一氧化二氮
营养循环
陆地生态系统
土壤生物学
生物量(生态学)
作者
Nathan Okoth Oduor,Ahmed S. Elrys,Manal A. Alnaimy,Tracy Opande,Di Feng,Yves Uwiragiye,Xiaoqian Dan,Shuirong Tang,Tongbin Zhu,Lei Meng,Jinbo Zhang,Christoph Müller
摘要
Salinity impairs soil health by disrupting microbial activity and altering soil physicochemical properties, ultimately undermining ecosystem resilience and productivity. Yet, the effect of salinity and its mitigation strategies on soil nitrogen (N) cycling and plant ammonium and nitrate uptake and N use efficiency is not well established on a global scale. Through a meta-analysis of 3422 paired observations from 309 publications, we found that salinity significantly alters soil N dynamics across multiple pathways. It inhibited the nitrification process by reducing microbial biomass, leading to a substantial accumulation of ammonium (+145%) and nitrite (+203%), while significantly suppressing biological N fixation (-82%). These shifts significantly increased plant uptake of ammonium but reduced that of nitrate and total N, ultimately contributing to a decline in crop yield by 9.5%. Accumulated ammonium in soil also increased ammonia volatilization by 158%. The effect of salinity on soil N availability was context-specific, exhibiting greater effects under high salinity levels, especially in natural ecosystems, arid zones, and alkaline soils. Contrastingly, salinity mitigation treatments led to significant improvements across multiple N pathways. They enhanced soil N pools, including increased biological N fixation and available and total N concentrations. These changes supported greater plant N uptake, resulting in increased N use efficiency and crop yield. However, these benefits were accompanied by a significant increase in nitrous oxide emissions by 80%, indicating a trade-off between environmental impacts and productivity gains. These effects of salinity mitigation treatments on N cycling were more pronounced under the application of organic and mineral fertilizers, as well as crop growth promoters. Collectively, our findings indicate that while salinity appears to impair N cycling by reducing microbial biomass and limiting plant N assimilation, these effects are reversible through mitigation measures. However, further investigation is required to develop salinity mitigation approaches that concurrently minimize nitrous oxide emissions.
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