Differential effects of N addition on the stoichiometry of microbes and extracellular enzymes in the rhizosphere and bulk soils of an alpine shrubland

被引:55
|
作者
Zhu, Xiaomin [1 ,2 ]
Liu, Mei [1 ,2 ,3 ,4 ,5 ]
Kou, Yongping [1 ,2 ]
Liu, Dongyan [1 ,2 ]
Liu, Qing [1 ,2 ]
Zhang, Ziliang [6 ]
Jiang, Zheng [1 ,2 ,5 ]
Yin, Huajun [1 ,2 ]
机构
[1] Chinese Acad Sci, Key Lab Mt Ecol Restorat & Bioresource Utilizat, Chengdu 610041, Sichuan, Peoples R China
[2] Chinese Acad Sci, Ecol Restorat Biodivers Conservat Key Lab Sichuan, China Croatia Belt & Rd Joint Lab Biodivers & Eco, Chengdu Inst Biol, Chengdu 610041, Sichuan, Peoples R China
[3] Sichuan Univ, Coll Life Sci, Chengdu 610064, Sichuan, Peoples R China
[4] Mianyang Normal Univ, Ecol Secur & Protect Key Lab Sichuan Prov, Mianyang 621000, Sichuan, Peoples R China
[5] Univ Chinese Acad Sci, Beijing 100049, Peoples R China
[6] Clemson Univ, Dept Plant & Environm Sci, Clemson, SC USA
基金
中国国家自然科学基金;
关键词
Rhizosphere and bulk soils; Microbial and enzymatic stoichiometry; Nitrogen addition; Alpine shrubland; The Qinghai-Tibet plateau; SIBIRAEA-ANGUSTATA SCRUB; NITROGEN DEPOSITION; CARBON STORAGE; ECOENZYMATIC STOICHIOMETRY; NUTRIENT ACQUISITION; EXTRACTION METHOD; P STOICHIOMETRY; BIOMASS; FOREST; RESPONSES;
D O I
10.1007/s11104-020-04468-6
中图分类号
S3 [农学(农艺学)];
学科分类号
0901 ;
摘要
Background and aims While large differences in microbial biomass and extracellular enzyme activities (EEAs) between rhizosphere and bulk soils have been demonstrated, the potentially different response of microbes and their EEAs in rhizosphere and bulk soils to nitrogen (N) deposition is still not elucidated. Methods We analyzed the microbial biomass and EEAs in the rhizosphere and bulk soils of Sibiraea angustata in an alpine shrubland on the eastern Qinghai-Tibet Plateau after chronic N application. We also analyzed the stoichiometric linkages between plants, microbes, enzymes and soils to clarify the coupled responses of aboveground plants and belowground ecological processes. Results Microbial nutrient concentrations and activities of EAAs responded differently to N addition in the rhizosphere and bulk soils. In the rhizosphere, N addition caused a significant increase in microbial biomass carbon (C), N and phosphorus (P) concentrations and greater P-degrading enzyme activity (relative to the activities of C- and N-degrading enzymes), which induced a significant reduction in enzyme C:P and N:P ratios. The rhizosphere enzyme N:P ratio was negatively correlated with the N:P ratios of plant, soil and microbe, implying that increased plant and microbial P uptake under N addition may gradually aggravate rhizosphere P limitation. However, for the bulk soil, N addition did not affect microbial biomass but significantly enhanced C-degrading enzyme activity and decreased the enzyme C:N ratio. Meanwhile, the bulk-soil enzyme C:N ratio was negatively correlated with the soil C:N ratio but independent of the plant C:N ratio, implying that N addition may enhance bulk-soil microbial C limitation. Conclusions Our study suggests that elevated N deposition may induce differential microbial nutrient limitation between the rhizosphere and bulk soils due to the plant-microbe-soil interactions in the rhizosphere. This study highlights the importance of incorporating rhizosphere microbial processes into biogeochemical models describing environmental changes.
引用
收藏
页码:285 / 301
页数:17
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