Zhang Yeye, Ren Yunfei, Zhou Shenglin, Ning Xiaoyu, Wang Xiukang, Yang Yanming, Sun Shikun, Vinay Nangia, Bahn Michael, Han Juan, Liu Yang, Xiong Youcai, Liao Yuncheng, Mo Fei
College of Agronomy, Northwest A&F University, Yangling, Shaanxi 712100, PR China.
College of Life Sciences, Yan'an University, Yan'an 716000, PR China.
Sci Total Environ. 2024 May 15;925:171564. doi: 10.1016/j.scitotenv.2024.171564. Epub 2024 Mar 8.
Tillage intensity significantly influences the heterogeneous distribution and dynamic changes of soil microorganisms, consequently shaping spatio-temporal patterns of SOC decomposition. However, little is known about the microbial mechanisms by which tillage intensity regulates the priming effect (PE) dynamics in heterogeneous spatial environments such as aggregates. Herein, a microcosm experiment was established by adding C-labeled straw residue to three distinct aggregate-size classes (i.e., mega-, macro-, and micro-aggregates) from two long-term contrasting tillage histories (no-till [NT] and conventional plow tillage [CT]) for 160 days to observe the spatio-temporal variations in PE. Metagenomic sequencing and Fourier transform mid-infrared techniques were used to assess the relative importance of C-degrading functional genes, microbial community succession, and SOC chemical composition in the aggregate-associated PE dynamics during straw decomposition. Spatially, straw addition induced a positive PE for all aggregates, with stronger PE occurring in larger aggregates, especially in CT soil compared to NT soil. Larger aggregates have more unique microbial communities enriched in genes for simple C degradation (e.g., E5.1.3.6, E2.4.1.7, pmm-pgm, and KduD in Nitrosospeera and Burkholderia), contributing to the higher short-term PE; however, CT soils harbored more genes for complex C degradation (e.g., TSTA3, fcl, pmm-pgm, and K06871 in Gammaproteobacteria and Phycicoccus), supporting a stronger long-term PE. Temporally, soil aggregates played a significant role in the early-stage PEs (i.e., < 59 days after residue addition) through co-metabolism and nitrogen (N) mining, as evidenced by the increased microbial biomass C and dissolved organic C (DOC) and reduced inorganic N with increasing aggregate-size class. At a later stage, however, the legacy effect of tillage histories controlled the PEs via microbial stoichiometry decomposition, as suggested by the higher DOC-to-inorganic N and DOC-to-available P stoichiometries in CT than NT. Our study underscores the importance of incorporating both spatial and temporal microbial dynamics for a comprehensive understanding of the mechanisms underlying SOC priming, especially in the context of long-term contrasting tillage practices.
耕作强度显著影响土壤微生物的异质分布和动态变化,从而塑造土壤有机碳分解的时空模式。然而,对于耕作强度在团聚体等异质空间环境中调节激发效应(PE)动态的微生物机制,我们知之甚少。在此,通过向来自两种长期对比耕作历史(免耕[NT]和传统翻耕[CT])的三个不同团聚体大小类别(即大团聚体、大团聚体和微团聚体)添加碳标记的秸秆残体,建立了一个微观实验,为期160天,以观察PE的时空变化。宏基因组测序和傅里叶变换中红外技术用于评估秸秆分解过程中与团聚体相关的PE动态中碳降解功能基因、微生物群落演替和土壤有机碳化学成分的相对重要性。在空间上,添加秸秆对所有团聚体都诱导了正的PE,在较大团聚体中PE更强,特别是与NT土壤相比,CT土壤中的团聚体。较大的团聚体有更多独特的微生物群落,富含简单碳降解基因(如亚硝化螺菌属和伯克霍尔德菌属中的E5.1.3.6、E2.4.1.7、pmm-pgm和KduD),导致更高的短期PE;然而,CT土壤中含有更多复杂碳降解基因(如γ-变形菌属和嗜盐球菌属中的TSTA3、fcl、pmm-pgm和K06871),支持更强的长期PE。在时间上,土壤团聚体在早期PE(即添加残体后<59天)中通过共代谢和氮(N)挖掘发挥了重要作用,这通过微生物生物量碳和溶解有机碳(DOC)的增加以及随着团聚体大小类别的增加无机氮的减少得到证明。然而,在后期,耕作历史的遗留效应通过微生物化学计量分解控制了PE,这由CT中比NT更高的DOC与无机氮和DOC与有效磷化学计量比表明。我们的研究强调了纳入空间和时间微生物动态对于全面理解土壤有机碳激发机制的重要性,特别是在长期对比耕作实践的背景下。