Long-term successive biochar application increases plant lignin and microbial necromass accumulation but decreases their contributions to soil organic carbon in rice–wheat cropping system

IF 5.9 3区 工程技术 Q1 AGRONOMY
Zhaoming Chen, Lili He, Jinchuan Ma, Junwei Ma, Jing Ye, Qiaogang Yu, Ping Zou, Wanchun Sun, Hui Lin, Feng Wang, Xu Zhao, Qiang Wang
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Abstract

Biochar application is widely recognized as an effective approach for increasing soil organic carbon (SOC) and mitigating climate change in agroecosystems. However, the effects of biochar application on net accumulations and relative contributions of different SOC sources remain unclear. Here, we explored the effects of biochar application on plant-derived (PDC) and microbial necromass C (MNC) in a 10-year experimental rice–wheat rotation field receiving four different intensities of biochar application (0, 2.25, 11.5, and 22.5 t ha−1 for each crop season), using phospholipid fatty acids (PLFAs), lignin phenols and amino sugars as biomarkers of microbial biomass, PDC and MNC, respectively. Our results showed that biochar application increased SOC content and stock by 32.6%–203% and 26.4%–145%, respectively. Higher biochar application (11.5 and 22.5 t ha−1) increased soil pH, total nitrogen (TN), total phosphorus (TP), SOC/TN, and root biomass. In addition, higher biochar application enhanced bacterial, fungal, and total microbial biomass. Plant lignin phenols and MNC contents significantly increased, whereas their contributions to SOC significantly decreased with the increase in biochar application rates due to the disproportionate increase in PDC and MNC, and SOC. Fungal necromass had a greater contribution to SOC than bacterial necromass. The fungal/bacterial necromass decreased from 2.56 to 2.26 with increasing biochar application rates, because of the higher abundances of bacteria than that of fungi as indicated by PLFAs under higher biochar application rates. Random forest analyses revealed that pH, TP, and SOC/TN were the main factors controlling plant lignin and MNC accumulation. Structural equation modeling revealed that biochar application increased lignin phenols by stimulating root biomass, whereas enhanced MNC accumulation was primarily from increased microbial biomass and lignin phenols. Overall, our findings suggest that biochar application increases the accumulation of the two SOC sources but decreases their contributions to SOC in paddy soils.

Abstract Image

在水稻-小麦种植系统中,长期连续施用生物炭可增加植物木质素和微生物坏死物质的积累,但会降低它们对土壤有机碳的贡献率
生物炭的应用被广泛认为是在农业生态系统中增加土壤有机碳(SOC)和减缓气候变化的有效方法。然而,施用生物炭对不同 SOC 来源的净积累和相对贡献的影响仍不清楚。在此,我们以磷脂脂肪酸(PLFAs)、木质素酚和氨基糖分别作为微生物生物量、PDC 和 MNC 的生物标记,探讨了施用生物炭对稻麦轮作 10 年试验田中施用四种不同强度生物炭(每季施用量分别为 0、2.25、11.5 和 22.5 吨/公顷)的植物源 C(PDC)和微生物尸质 C(MNC)的影响。结果表明,施用生物炭可使 SOC 含量和存量分别增加 32.6%-203% 和 26.4%-145% 。较高的生物炭施用量(11.5 吨/公顷和 22.5 吨/公顷)可提高土壤 pH 值、全氮(TN)、全磷(TP)、SOC/TN 和根系生物量。此外,施用更多生物炭还能提高细菌、真菌和微生物总生物量。随着生物炭施用量的增加,植物木质素酚和 MNC 的含量显著增加,而它们对 SOC 的贡献却显著减少,原因是 PDC 和 MNC 以及 SOC 的增加不成比例。真菌新菌体对 SOC 的贡献大于细菌新菌体。随着生物炭施用率的增加,真菌/细菌新陈代谢量从 2.56 降至 2.26,这是因为在生物炭施用率较高的情况下,PLFAs 显示细菌的丰度高于真菌。随机森林分析表明,pH、TP 和 SOC/TN 是控制植物木质素和 MNC 积累的主要因素。结构方程模型显示,施用生物炭可通过刺激根部生物量来增加木质素酚,而 MNC 积累的增加主要来自微生物生物量和木质素酚的增加。总之,我们的研究结果表明,施用生物炭可增加两种 SOC 来源的积累,但会降低它们对稻田土壤中 SOC 的贡献。
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来源期刊
Global Change Biology Bioenergy
Global Change Biology Bioenergy AGRONOMY-ENERGY & FUELS
CiteScore
10.30
自引率
7.10%
发文量
96
审稿时长
1.5 months
期刊介绍: GCB Bioenergy is an international journal publishing original research papers, review articles and commentaries that promote understanding of the interface between biological and environmental sciences and the production of fuels directly from plants, algae and waste. The scope of the journal extends to areas outside of biology to policy forum, socioeconomic analyses, technoeconomic analyses and systems analysis. Papers do not need a global change component for consideration for publication, it is viewed as implicit that most bioenergy will be beneficial in avoiding at least a part of the fossil fuel energy that would otherwise be used. Key areas covered by the journal: Bioenergy feedstock and bio-oil production: energy crops and algae their management,, genomics, genetic improvements, planting, harvesting, storage, transportation, integrated logistics, production modeling, composition and its modification, pests, diseases and weeds of feedstocks. Manuscripts concerning alternative energy based on biological mimicry are also encouraged (e.g. artificial photosynthesis). Biological Residues/Co-products: from agricultural production, forestry and plantations (stover, sugar, bio-plastics, etc.), algae processing industries, and municipal sources (MSW). Bioenergy and the Environment: ecosystem services, carbon mitigation, land use change, life cycle assessment, energy and greenhouse gas balances, water use, water quality, assessment of sustainability, and biodiversity issues. Bioenergy Socioeconomics: examining the economic viability or social acceptability of crops, crops systems and their processing, including genetically modified organisms [GMOs], health impacts of bioenergy systems. Bioenergy Policy: legislative developments affecting biofuels and bioenergy. Bioenergy Systems Analysis: examining biological developments in a whole systems context.
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