Wieczorek Adam S, Schmidt Oliver, Chatzinotas Antonis, von Bergen Martin, Gorissen Antonie, Kolb Steffen
Department of Ecological Microbiology, University of Bayreuth, Bayreuth, Germany.
Department of Environmental Microbiology, Helmholtz Centre for Environmental Research-UFZ, Leipzig, Germany.
Front Microbiol. 2019 Jun 20;10:1293. doi: 10.3389/fmicb.2019.01293. eCollection 2019.
Chitin provides a valuable carbon and nitrogen source for soil microorganisms and is a major component of particulate organic matter in agricultural soils. To date, there is no information on interaction and interdependence in chitin-degrading soil microbiomes. Since microbial chitin degradation occurs under both oxic and anoxic conditions and both conditions occur simultaneously in soil, the comparison of the active microbiome members under both conditions can reveal key players for the overall degradation in aerated soil. A time-resolved 16S rRNA stable isotope probing experiment was conducted with soil material from the top soil layer of a wheat-covered field. [C]-chitin was largely mineralized within 20 days under oxic conditions. , , and several families were identified as initially active chitin degraders. Subsequently, and were labeled by assimilation of C carbon either from [C]-chitin or from C-enriched components of primary chitin degraders. Bacterial predators (e.g., and ) were labeled, too, and non-labeled microeukaryotic predators () increased their relative abundance toward the end of the experiment (70 days), indicating that chitin degraders were subject to predation. Trophic interactions differed substantially under anoxic and oxic conditions. Various fermentation types occurred along with iron respiration. While and were the first taxa to be labeled, although at a low C level, and uncultured were predominantly labeled at a much higher C level during the later stages, suggesting that the latter two bacterial taxa were mainly responsible for the degradation of chitin and also provided substrates for iron reducers. Eventually, our study revealed that (1) hitherto unrecognized were involved in a chitin-degrading microbial food web of an agricultural soil, (2) trophic interactions were substantially shaped by the oxygen availability, and (3) detectable predation was restricted to oxic conditions. The gained insights into trophic interactions foster our understanding of microbial chitin degradation, which is in turn crucial for an understanding of soil carbon dynamics.
几丁质为土壤微生物提供了宝贵的碳源和氮源,是农业土壤中颗粒有机物的主要成分。迄今为止,关于几丁质降解土壤微生物群落中的相互作用和相互依存关系尚无相关信息。由于微生物几丁质降解在有氧和无氧条件下均可发生,且这两种条件在土壤中同时存在,因此比较这两种条件下的活性微生物群落成员可以揭示通气土壤中整体降解的关键参与者。我们对一片种植小麦的田地表层土壤进行了一项时间分辨的16S rRNA稳定同位素探测实验。[¹³C] - 几丁质在有氧条件下20天内大部分被矿化。[¹³C] - 几丁质在有氧条件下20天内大部分被矿化。[¹³C] - 几丁质在有氧条件下20天内大部分被矿化。芽孢杆菌属、伯克氏菌属和几个科被确定为最初活跃的几丁质降解菌。随后,噬纤维菌属和黄杆菌属通过同化来自[¹³C] - 几丁质或初级几丁质降解菌的¹³C富集成分中的碳而被标记。细菌捕食者(如蛭弧菌属和嗜几丁质杆菌属)也被标记,未被标记的微型真核捕食者(尖鼻虫属)在实验后期(70天)其相对丰度增加,这表明几丁质降解菌受到了捕食。在无氧和有氧条件下,营养相互作用存在显著差异。各种发酵类型与铁呼吸同时发生。虽然伯克氏菌属和芽孢杆菌属是最早被标记的分类群,尽管¹³C水平较低,但噬纤维菌属和未培养的黄杆菌属在后期以高得多的¹³C水平被大量标记,这表明后两个细菌分类群主要负责几丁质的降解,并且还为铁还原菌提供了底物。最终,我们的研究表明:(1)迄今为止未被认识的噬纤维菌属参与了农业土壤的几丁质降解微生物食物网;(2)营养相互作用在很大程度上受氧气可用性的影响;(3)可检测到的捕食仅限于有氧条件。对营养相互作用的深入了解促进了我们对微生物几丁质降解的理解,而这反过来对于理解土壤碳动态至关重要。