Soil recalcitrant but not labile organic nitrogen mineralization contributes to microbial nitrogen immobilization and plant nitrogen uptake

被引:1
|
作者
Chen, Shending [1 ,2 ,3 ]
Elrys, Ahmed S. [1 ,4 ,5 ,6 ]
Yang, Wenyan [1 ,2 ]
Du, Siwen [2 ]
He, Mengqiu [2 ]
Cai, Zucong [2 ]
Zhang, Jinbo [1 ,2 ,4 ,6 ]
Mueller, Christoph [3 ,6 ,7 ]
机构
[1] Hainan Univ, Sch Breeding & Multiplicat, Sanya 572025, Peoples R China
[2] Nanjing Normal Univ, Sch Geog, Nanjing, Peoples R China
[3] Justus Liebig Univ Giessen, Inst Plant Ecol, Giessen, Germany
[4] Hainan Univ, Coll Trop Agr & Forestry, Haikou, Peoples R China
[5] Zagazig Univ, Fac Agr, Soil Sci Dept, Zagazig, Egypt
[6] Justus Liebig Univ, Liebig Ctr Agroecol & Climate Impact Res, Giessen, Germany
[7] Univ Coll Dublin, Sch Biol & Environm Sci & Earth Inst, Dublin, Ireland
基金
中国国家自然科学基金;
关键词
N-15 tracing studies; ecosystem nitrogen retention; mineral-associated organic matter; nitrogen mineralization; particulate organic matter; plant nitrogen uptake; ATMOSPHERIC CARBON-DIOXIDE; N TRANSFORMATION RATES; TEMPERATURE SENSITIVITY; TERRESTRIAL ECOSYSTEMS; MACROORGANIC MATTER; ENZYME-ACTIVITIES; CYCLE FEEDBACKS; N2O EMISSIONS; FOREST SOILS; RHIZOSPHERE;
D O I
10.1111/gcb.17290
中图分类号
X176 [生物多样性保护];
学科分类号
090705 ;
摘要
Soil organic nitrogen (N) mineralization not only supports ecosystem productivity but also weakens carbon and N accumulation in soils. Recalcitrant (mainly mineral-associated organic matter) and labile (mainly particulate organic matter) organic materials differ dramatically in nature. Yet, the patterns and drivers of recalcitrant (M-Nrec) and labile (M-Nlab) organic N mineralization rates and their consequences on ecosystem N retention are still unclear. By collecting M-Nrec (299 observations) and M-Nlab (299 observations) from 57 N-15 tracing studies, we found that soil pH and total N were the master factors controlling M-Nrec and M-Nlab, respectively. This was consistent with the significantly higher rates of M-Nrec in alkaline soils and of M-Nlab in natural ecosystems. Interestingly, our analysis revealed that M-Nrec directly stimulated microbial N immobilization and plant N uptake, while M-Nlab stimulated the soil gross autotrophic nitrification which discouraged ammonium immobilization and accelerated nitrate production. We also noted that M-Nrec was more efficient at lower precipitation and higher temperatures due to increased soil pH. In contrast, M-Nlab was more efficient at higher precipitation and lower temperatures due to increased soil total N. Overall, we suggest that increasing M-Nrec may lead to a conservative N cycle, improving the ecosystem services and functions, while increasing M-Nlab may stimulate the potential risk of soil N loss.
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页数:17
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