Tang Zuoxin, Sun Xiaolu, Luo Zhongkui, He Nianpeng, Sun Osbert Jianxin
College of Forest Science Beijing Forestry University Beijing China.
CSIRO Agriculture & Food Canberra Australia.
Ecol Evol. 2017 Dec 10;8(2):879-891. doi: 10.1002/ece3.3708. eCollection 2018 Jan.
How biotic and abiotic factors influence soil carbon (C) mineralization rate () has recently emerged as one of the focal interests in ecological studies. To determine the relative effects of temperature, soil substrate and microbial community on , we conducted a laboratory experiment involving reciprocal microbial inoculations of three zonal forest soils, and measured over a 61-day period at three temperatures (5, 15, and 25°C). Results show that both and the cumulative emission of C (), normalized to per unit soil organic C (SOC), were significantly affected by incubation temperature, soil substrate, microbial inoculum treatment, and their interactions (<.05). Overall, the incubation temperature had the strongest effect on the ; at given temperatures, soil substrate, microbial inoculum treatment, and their interaction all significantly affected both (<.001) and (≤.01), but the effect of soil substrate was much stronger than others. There was no consistent pattern of thermal adaptation in microbial decomposition of SOC in the reciprocal inoculations. Moreover, when different sources of microbial inocula were introduced to the same soil substrate, the microbial community structure converged with incubation without altering the overall soil enzyme activities; when different types of soil substrate were inoculated with the same sources of microbial inocula, both the microbial community structure and soil enzyme activities diverged. Overall, temperature plays a predominant role in affecting and , while soil substrate determines the mineralizable SOC under given conditions. The role of microbial community in driving SOC mineralization is weaker than that of climate and soil substrate, because soil microbial community is both affected, and adapts to, climatic factors and soil matrix.
生物和非生物因素如何影响土壤碳(C)矿化速率()最近已成为生态研究的重点关注领域之一。为了确定温度、土壤底物和微生物群落对的相对影响,我们进行了一项实验室实验,对三种地带性森林土壤进行了相互的微生物接种,并在三个温度(5、15和25°C)下测量了61天的。结果表明,以单位土壤有机碳(SOC)标准化后的和C的累积排放量()均受到培养温度、土壤底物、微生物接种处理及其相互作用的显著影响(<.05)。总体而言,培养温度对的影响最强;在给定温度下,土壤底物、微生物接种处理及其相互作用均对和(<.001)以及(≤.01)有显著影响,但土壤底物的影响比其他因素要强得多。在相互接种中,SOC的微生物分解没有一致的热适应模式。此外,当将不同来源的微生物接种物引入相同的土壤底物时,微生物群落结构随着培养而趋同,而不会改变整体土壤酶活性;当用相同来源的微生物接种物接种不同类型的土壤底物时,微生物群落结构和土壤酶活性都会发生分化。总体而言,温度在影响和方面起主要作用,而土壤底物在给定条件下决定了可矿化的SOC。微生物群落在驱动SOC矿化中的作用比气候和土壤底物的作用弱,因为土壤微生物群落既受到气候因素和土壤基质的影响,又适应它们。