Secondary shrubs promoted the priming effect by increasing soil particle organic carbon mineralization

IF 2.7 3区 农林科学 Q2 ECOLOGY Frontiers in Forests and Global Change Pub Date : 2023-11-13 DOI:10.3389/ffgc.2023.1288259
Qinghui Yu, Zixu Zhang, Yuan He, Ming Hao, Guifang Wang, Xingjian Dun, Qicong Wu, Peng Gao
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Abstract

Introduction Inputs of additional organic matter to the soil will accelerate or inhibit the decomposition of soil organic carbon (SOC), resulting in a priming effect (PE), which is a key mechanism affecting soil carbon (C) cycling. The impact mechanism of changes in soil properties on the PE is still unclear after vegetation restoration; in particular, the contribution of C pools with different turnover rates to the PE has not been distinguished and quantified. Methods In this study, the secondary shrub (SB) ( Vitex negundo var. heterophylla ) formed by the enclosure of barren grassland was selected as the research object, and the barren grassland (GL) was taken as the control. Equal amounts of 13 C-labeled glucose were added to the topsoil for a 45-day incubation experiment to measure the PE. Moreover, soil samples were destructively sampled to explore the fate of new C and changes in POC and MAOC fractions during incubation. Results After 45 days of incubation, most of the new C formed by glucose flowed to MAOC, with 95.45% in SB soil and 92.29% in GL soil. In the experiment, all soils showed a positive PE. The PE, POC mineralization and MAOC accumulation were higher in SB soil than in GL soil. During incubation, the mineralization of POC was positively correlated with the PE and made a major contribution to the PE. Partial correlation analysis showed that after vegetation restoration, SB further promoted the mineralization of POC by increasing the soil moisture, fungal diversity and necromass C of bacteria, which led to an increase in PE. Conclusion The SB mainly enhanced PE by increasing soil fungal diversity and mineralization of POC. And increasing PE due to the SB may lead to an increase in soil C emissions. Therefore, we need to adopt forest management and other measures to address the potential risks of increased soil C emissions in the vegetation restoration process.
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次生灌木通过增加土壤颗粒有机碳矿化,促进了土壤的启动效应
土壤中额外有机质的输入会加速或抑制土壤有机碳(SOC)的分解,产生启动效应(PE),这是影响土壤碳(C)循环的关键机制。植被恢复后土壤性质变化对PE的影响机制尚不清楚;特别是,不同周转率的C池对PE的贡献尚未得到区分和量化。方法以荒草草地封育后形成的次生灌木(SB)为研究对象,以荒草草地(GL)为对照。在表土中加入等量的13 c标记葡萄糖,进行45天的培养实验,以测量PE。此外,对土壤样品进行破坏性采样,以探索新C的命运以及POC和MAOC在孵育过程中的变化。结果培养45 d后,葡萄糖形成的新C大部分流向MAOC,其中SB土壤为95.45%,GL土壤为92.29%。试验中,所有土壤PE均呈阳性。SB土壤PE、POC矿化和MAOC积累量高于GL土壤。在孵育期间,POC的矿化与PE呈正相关,是PE的主要来源。偏相关分析表明,植被恢复后,SB通过增加土壤水分、真菌多样性和细菌坏死质C进一步促进POC的矿化,从而导致PE的增加。结论SB主要通过增加土壤真菌多样性和POC矿化来增强PE。土壤碳排放量的增加可能会导致土壤碳排放量的增加。因此,我们需要采取森林管理等措施来解决植被恢复过程中土壤C排放增加的潜在风险。
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来源期刊
CiteScore
4.50
自引率
6.20%
发文量
256
审稿时长
12 weeks
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