硝化作用
铵
自行车
氮气循环
硝酸盐
环境科学
环境化学
陆地生态系统
土壤水分
生态系统
湿地
矿化(土壤科学)
氮气
温带气候
草原
农学
土壤有机质
生态学
植物群落
土壤酸化
土壤pH值
陆生植物
初级生产
营养循环
生物地球化学循环
温带森林
氨
土工试验
作者
Ahmed S. Elrys,Lei Meng,Yves Uwiragiye,Khaled A. El‐Tarabily,Qilin Zhu,Xiaoqian Dan,Tang Shuirong,Wu Yanzheng,Yanfu Bai,Tongbin Zhu,Jinbo Zhang,Christoph Müller
摘要
Reliable prediction of plant nitrogen (N) acquisition strategies is critical for interpreting ecosystem productivity. We propose a process-based framework that connects plant N preferences to soil microbial N cycling and environmental conditions. We compiled data from 66 15N labeling studies, yielding 336 triplet observations, each consisting of plant organic-N, ammonium-N, and nitrate-N uptake measurements (Dataset 1). Additionally, 2030 observations of gross soil N transformations from 270 studies were compiled to predict the spatial variation of these rates globally, with the aim of populating Dataset 1. We found that ammonium-N was the primary contributor to N uptake in forests (49% ± 1.84%) and wetlands (55% ± 3.29%), whereas nitrate-N was the dominant source in grasslands (41% ± 1.52%). Plant ammonium-N and nitrate-N preferences were lowest in temperate and tropical regions, respectively. Nitrification capacity-autotrophic nitrification (the process where ammonium is oxidized to nitrate) to gross N mineralization (GNM; the conversion of organic N to ammonium) ratio-was the main regulator of plant ammonium-N and nitrate-N preferences. Terrestrial environments with high nitrification capacity (e.g., temperate or grassland soils) resulting from high soil pH and low carbon-to-N ratio exhibited higher plant nitrate-N preference, while adverse conditions (e.g., tropical, forest, or wetland soils) exhibited higher ammonium-N preference. Interestingly, dissimilatory nitrate reduction to ammonium (DNRA) process redirected plant preference toward ammonium-based nutrition in organic carbon-rich, low-oxygen soils. Climate-driven shifts in plant N preference are mediated by gross soil N transformations, as increased precipitation and/or temperature accelerated GNM and/or DNRA while inhibiting nitrification capacity, promoting plant ammonium preference. Soil N cycling and environmental conditions explained little variation in plant organic-N preference, suggesting that other variables (e.g., mycorrhizal associations and plant functional traits) may be at play. We highlight that plant N acquisition is not purely plant-driven, but it mirrors underground N transformations, with environmental conditions acting as pivotal modulators of this relationship.
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