首页> 外文期刊>Microbial Ecology: An International Journal >Temporal Changes in Soil Bacterial Diversity and Humic Substances Degradation in Subarctic Tundra Soil
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Temporal Changes in Soil Bacterial Diversity and Humic Substances Degradation in Subarctic Tundra Soil

机译:北极苔原土壤中细菌多样性和腐殖质降解的时间变化

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Humic substances (HS), primarily humic acids (HA) and fulvic acids (FA), are the largest constituent of soil organic matter. In microcosm systems with subarctic HS-rich tundra soil (site AK 1-75; approximately 5.6 A degrees C during the thawing period) from Council, Alaska, the HA content significantly decreased to 48 % after a 99-day incubation at 5 A degrees C as part of a biologically mediated process. Accordingly, levels of FA, a putative byproduct of HA degradation, consistently increased to 172 % during an identical incubation process. Culture-independent microbial community analysis showed that during the microcosm experiments, the relative abundance of phyla Proteobacteria (bacteria) and Euryarchaeota (archaea) largely increased, indicating their involvement in HS degradation. When the indigenous bacteria in AK 1-75 were enriched in an artificial mineral medium spiked with HA, the changes in relative abundance were most conspicuous in Proteobacteria (from 60.2 to 79.0 %), specifically Betaproteobacteria-related bacteria. One hundred twenty-two HA-degrading bacterial strains, primarily from the genera Paenibacillus (phylum Firmicutes) and Pseudomonas (class Gammaproteobacteria), were cultivated from AK 1-75 and nearby sites. Through culture-dependent analysis with these bacterial isolates, we observed increasing HS-degradation rates in parallel with rising temperatures in a range of 0 A degrees C to 20 A degrees C, with the most notable increase occurring at 8 A degrees C compared to 6 A degrees C. Our results indicate that, although microbial-mediated HS degradation occurs at temperature as low as 5 A degrees C in tundra ecosystems, increasing soil temperature caused by global climate change could enhance HS degradation rates. Extending the thawing period could also increase degradation activity, thereby directly affecting nearby microbial communities and rhizosphere environments.
机译:腐殖质(HS),主要是腐殖酸(HA)和黄腐酸(FA),是土壤有机质的最大成分。在来自阿拉斯加议会的富含弧化亚硫酸盐的冻土苔原土壤(AK 1-75站点;融化期间约为5.6 A摄氏度)的缩影系统中,在5 A摄氏度下孵育99天后,HA含量显着降低至48% C作为生物介导过程的一部分。因此,在相同的孵育过程中,作为HA降解的假定副产物FA的水平始终提高到172%。不依赖培养物的微生物群落分析表明,在微观实验中,菌群变形杆菌(细菌)和Euryarchaeota(古细菌)的相对丰度大大增加,表明它们参与了HS降解。当AK 1-75中的本地细菌在掺有HA的人工矿物培养基中富集时,变形杆菌中相对丰度的变化最为明显(从60.2%到79.0%),特别是Betaproteobacteria相关细菌。从AK 1-75和附近地点培养了一百二十二种降解HA的细菌菌株,主要来自Paenibacillus(Firmumticutes)和Pseudomonas(丙种丙种细菌)。通过对这些细菌分离株的依赖于培养物的分析,我们观察到,HS降解速率与0 A摄氏度至20 A摄氏度范围内的温度升高同时发生,与8摄氏度相比,最显着的升高发生在6摄氏度之间1摄氏度。我们的结果表明,虽然微生物介导的HS降解在苔原生态系统中的温度低至5 A摄氏度时发生,但全球气候变化引起的土壤温度升高可能会提高HS降解率。延长解冻时间也可能增加降解活性,从而直接影响附近的微生物群落和根际环境。

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