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Syntrophic Oxidation of Propionate in Rice Field Soil at 15 and 30°C under Methanogenic Conditions

机译:产甲烷条件下15和30°C下稻田土壤中丙酸的总养分氧化

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Propionate is one of the major intermediary products in the anaerobic decomposition of organic matter in wetlands and paddy fields. Under methanogenic conditions, propionate is decomposed through syntrophic interaction between proton-reducing and propionate-oxidizing bacteria and H_(2)-consuming methanogens. Temperature is an important environmental regulator; yet its effect on syntrophic propionate oxidation has been poorly understood. In the present study, we investigated the syntrophic oxidation of propionate in a rice field soil at 15°C and 30°C. [U-~(13)C]propionate (99 atom%) was applied to anoxic soil slurries, and the bacteria and archaea assimilating ~(13)C were traced by DNA-based stable isotope probing. Syntrophobacter spp., Pelotomaculum spp., and Smithella spp. were found significantly incorporating ~(13)C into their nucleic acids after [~(13)C]propionate incubation at 30°C. The activity of Smithella spp. increased in the later stage, and concurrently that of Syntrophomonas spp. increased. Aceticlastic Methanosaetaceae and hydrogenotrophic Methanomicrobiales and Methanocellales acted as methanogenic partners at 30°C. Syntrophic oxidation of propionate also occurred actively at 15°C. Syntrophobacter spp. were significantly labeled with ~(13)C, whereas Pelotomaculum spp. were less active at this temperature. In addition, Methanomicrobiales , Methanocellales , and Methanosarcinaceae dominated the methanogenic community, while Methanosaetaceae decreased. Collectively, temperature markedly influenced the activity and community structure of syntrophic guilds degrading propionate in the rice field soil. Interestingly, Geobacter spp. and some other anaerobic organisms like Rhodocyclaceae , Acidobacteria , Actinobacteria , and Thermomicrobia probably also assimilated propionate-derived ~(13)C. The mechanisms for the involvement of these organisms remain unclear.
机译:丙酸是湿地和稻田中有机物厌氧分解的主要中间产物之一。在产甲烷的条件下,丙酸通过质子还原和丙酸氧化细菌与消耗H_(2)的产甲烷菌之间的营养相互作用而分解。温度是重要的环境调节剂。然而,它对腐殖酸丙酸氧化的影响知之甚少。在本研究中,我们研究了在15°C和30°C的稻田土壤中丙酸的同养氧化。将[U-〜(13)C]丙酸酯(99%(原子))应用于缺氧土壤浆液中,并通过基于DNA的稳定同位素探测来追踪与〜(13)C同化的细菌和古细菌。枯萎菌属,Pelotomaculum属和Smithella属。在30°C温育[〜(13)C]丙酸酯后,发现将〜(13)C显着掺入了其核酸。 Smithella spp的活动。在后期增加,并同时出现Syntrophomonas spp。增加。在30°C时,乙腈甲烷菌科和氢营养型甲烷微生物和甲烷菌充当产甲烷的伴侣。在15°C时,丙酸的同养氧化也很活跃。幽门螺杆菌被〜(13)C显着标记,而Pelotomaculum spp。在此温度下活性较低。另外,甲烷菌,甲烷菌和甲烷糖藻科占主导地位的产甲烷菌群落,而甲烷藻科则减少。总的来说,温度显着影响了稻田土壤中降解丙酸的同养公会的活性和群落结构。有趣的是,Geobacter spp。以及其他一些厌氧生物,例如红景天科,酸性细菌,放线菌和嗜热微生物,也可能吸收了丙酸衍生的〜(13)C。这些生物参与的机制仍不清楚。

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