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首页> 外文期刊>Biology and fertility of soils: Cooperating Journal of the International Society of Soil Science >Biochar decreased rhizodeposits stabilization via opposite effects on bacteria and fungi: diminished fungi-promoted aggregation and enhanced bacterial mineralization
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Biochar decreased rhizodeposits stabilization via opposite effects on bacteria and fungi: diminished fungi-promoted aggregation and enhanced bacterial mineralization

机译:生物炭通过对细菌和真菌的相反影响降低了Rhizodeposits稳定性:降低真菌促进的聚集和增强的细菌矿化

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Ryegrass was pulse-labeled with enriched (CO2)-C-13 for 18 h, followed by dynamic photosynthetic-carbon (C-13) quantification in the plant (shoot, root), soil aggregates (three size classes), and microbial phospholipids fatty acids (PLFA-SIP) in soil amended with or without 700 degrees C-pyrolyzed biochar. We observed that biochar led to no difference of C-13 allocation in shoot or root but reduced 88.7% of total C-13 in soil, with decreased incorporation by 92.8% (macroaggregates), 94.5% (microaggregates), and 84.1% (silt-clays), respectively, compared to biochar-unamended soil. Meanwhile, biochar exerted negative effects on fungal relative abundance but led to positive impacts on that of bacteria, e.g., it reduced root-associated fungi (i.e., 16:1 omega 5c) and fungal-assimilated C-13 (from averagely 71.2 ng C g(-1) soil to 26.3 ng C g(-1) soil after biochar application). The enhanced bacteria/fungi could be driven by biochar-mediated pH increase that relieved acid stress to bacteria. Co-occurrence network confirmed that biochar addition favored bacteria to compete with fungi, leading to decreased aggregation and stability (indicated by reduced normalized mean weight diameter) due to less fungal entangling with aggregates, thus exposing the rhizodeposits to bacterial (i.e., actinomycetes) decomposition. The correlation analysis further evidenced that fungal abundance was associated with C-13 accumulation in soil aggregates, while bacterial relative abundance especially that of actinomycetes was negatively correlated with C-13 accumulation. Random forest modeling (RF) supported the contributions of fungi to C-13-sequestration compared to bacteria. Taken together, we concluded that less stabilization of rhizodeposits in the biochar-amended soil was due to changes in microbial community, particularly the balance of fungi-bacteria and their interactions with soil physicochemical properties, i.e., aggregation and pH.
机译:Ryegrass用富含富含(CO2)-C-13的脉冲标记为18小时,然后在植物(芽,根),土壤聚集体(三种尺寸类)中的动态光合 - 碳(C-13)定量,以及微生物磷脂用或没有700摄氏度的生物炭修正的土壤中的脂肪酸(PLFA-SIP)。我们观察到生物炭导致芽或根部C-13分配的差异,但降低了土壤中C-13总量的88.7%,掺入掺入92.8%(大甲淀粉),94.5%(微烧结)和84.1%(淤泥与生物炭 - 未加工的土壤相比,分别 - Clays)。同时,生物炭对真菌相对丰度产生负面影响,但导致对细菌的积极影响,例如,它减少了根系相关的真菌(即16:1ω5C)和真菌同化的C-13(来自平均值71.2 Ng C.生物炭剂应用后,G(1)土壤至26.3ng C g(-1)土壤)。增强的细菌/真菌可以由生物淀果介导的pH增加,从而减轻酸性胁迫对细菌。共同发生网络证实,生物炭加入有利的细菌与真菌竞争,导致由于具有胚胎的真菌缠结较小而导致聚集和稳定性降低(由归一化平均重量直径的降低),从而将无根茎暴露于细菌(即,放线菌)分解。相关性分析进一步证明了真菌丰度与土壤聚集体的C-13积累相关,而细菌相对丰度尤其与C-13积累呈负相关。随机森林建模(RF)支持真菌与细菌相比封存的贡献。我们得出结论,生物炭修正土壤中的鼻塞稳定性较少是由于微生物群落的变化,特别是真菌细菌的平衡及其与土壤物理化学性质的相互作用,即聚集和pH。

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