Divergent accumulation of microbial necromass and plant lignin phenol induced by adding maize straw to fertilized soils

IF 6.1 1区 农林科学 Q1 SOIL SCIENCE
Xu Liu , Roland Bol , Tingting An , Yaocen Liu , Yingde Xu , Shuangyi Li , Jingkuan Wang
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引用次数: 0

Abstract

Plant carbon (C) inputs and their subsequent microbial transformation affect the build-up process of soil organic C (SOC) pool. Nevertheless, there are knowledge gaps on how crop straw addition modifies SOC composition at molecular-level, especially in soils with different fertilization practices. Here, long-term fertilized Mollisols (unfertilized control, NF; inorganic fertilization, IF; inorganic fertilization plus manure, IFM) were incubated with or without maize straw addition in a 900-day field mesocosm experiment. The microbial necromass and plant lignin components contents were synchronously quantified based on amino sugar and lignin phenol biomarkers, respectively. And changes in SOC chemical composition were examined using solid-state 13C nuclear magnetic resonance spectroscopy. Relative to the NF treatment, long-term fertilization increased amino sugar and lignin phenol contents, and manure application enhanced the accumulation of plant lignin components more than that of microbial necromass. Compared with the NF treatment, the IF treatment decreased the relative proportion of alkyl C and SOC content, suggesting that changes in microbial necromass and lignin phenol were not always consistent with changes in SOC. For the NF and IF treatments, maize straw incorporation increased both amino sugar content and its contribution to SOC, indicating that microbial anabolism was important for SOC accumulation after adding maize straw in C-poor soils. For the IFM treatment, maize straw addition decreased lignin phenol content (27 %) and its contribution to SOC but increased the contribution of amino sugar to SOC, reflecting an enlarged contribution of microbial necromass to soil C pool formation under manure application after maize straw addition. The contribution of lignin phenol to SOC was decreased from days 360–900, whereas fungal necromass C content and the contribution of amino sugar to SOC were increased from days 360–900 under the IFM soil with maize straw addition, indicating that plant lignin components might be converted into fungal biomass and its necromass with increasing maize straw decomposition under manure application. Overall, we concluded that maize straw addition favored microbial immobilization in all fertilization treatments.

在施肥土壤中添加玉米秸秆诱导微生物坏死物质和植物木质素酚的差异积累
植物碳(C)的输入及其随后的微生物转化会影响土壤有机碳(SOC)库的积累过程。然而,关于作物秸秆的添加如何在分子水平上改变土壤有机碳的组成,尤其是在不同施肥方法的土壤中,目前还存在知识空白。在此,在为期 900 天的田间中观实验中,对长期施肥的莫利溶胶土壤(未施肥对照,NF;无机施肥,IF;无机施肥加粪肥,IFM)进行了添加或不添加玉米秸秆的培养。根据氨基糖和木质素酚生物标记,分别同步量化了微生物坏死物质和植物木质素成分的含量。并利用固态 13C 核磁共振光谱分析了 SOC 化学成分的变化。与 NF 处理相比,长期施肥增加了氨基酸糖和木质素酚的含量,施用粪肥对植物木质素成分积累的促进作用大于微生物坏死物。与 NF 处理相比,IF 处理降低了烷基 C 和 SOC 含量的相对比例,这表明微生物坏死物和木质素酚的变化并不总是与 SOC 的变化一致。在 NF 和 IF 处理中,玉米秸秆的加入增加了氨基糖的含量及其对 SOC 的贡献,表明在贫碳土壤中加入玉米秸秆后,微生物的新陈代谢对 SOC 的积累很重要。在 IFM 处理中,玉米秸秆的加入降低了木质素酚含量(27%)及其对 SOC 的贡献率,但增加了氨基酸糖对 SOC 的贡献率,这反映了在加入玉米秸秆后施用粪肥的条件下,微生物坏死物质对土壤 C 池形成的贡献率增大。在添加玉米秸秆的 IFM 土壤中,木质素酚对 SOC 的贡献在第 360-900 天减少,而真菌坏质 C 含量和氨基糖对 SOC 的贡献在第 360-900 天增加,这表明在施用粪肥的条件下,随着玉米秸秆腐烂程度的增加,植物木质素成分可能转化为真菌生物量及其坏质。总之,我们得出结论,在所有施肥处理中,玉米秸秆的添加都有利于微生物固定化。
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来源期刊
Soil & Tillage Research
Soil & Tillage Research 农林科学-土壤科学
CiteScore
13.00
自引率
6.20%
发文量
266
审稿时长
5 months
期刊介绍: Soil & Tillage Research examines the physical, chemical and biological changes in the soil caused by tillage and field traffic. Manuscripts will be considered on aspects of soil science, physics, technology, mechanization and applied engineering for a sustainable balance among productivity, environmental quality and profitability. The following are examples of suitable topics within the scope of the journal of Soil and Tillage Research: The agricultural and biosystems engineering associated with tillage (including no-tillage, reduced-tillage and direct drilling), irrigation and drainage, crops and crop rotations, fertilization, rehabilitation of mine spoils and processes used to modify soils. Soil change effects on establishment and yield of crops, growth of plants and roots, structure and erosion of soil, cycling of carbon and nutrients, greenhouse gas emissions, leaching, runoff and other processes that affect environmental quality. Characterization or modeling of tillage and field traffic responses, soil, climate, or topographic effects, soil deformation processes, tillage tools, traction devices, energy requirements, economics, surface and subsurface water quality effects, tillage effects on weed, pest and disease control, and their interactions.
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