Department of Environmental Biotechnology, UFZ, Helmholtz Centre for Environmental Research, Permoserstrasse 15, D-04318 Leipzig, Germany.
Appl Environ Microbiol. 2010 Dec;76(24):8222-30. doi: 10.1128/AEM.01632-10. Epub 2010 Oct 29.
Removal of potential pathogenic bacteria, for example, during wastewater treatment, is effected by sorption, filtration, natural die-off, lysis by viruses, and grazing by protists, but the actual contribution of grazing has never been assessed quantitatively. A methodical approach for analyzing the grazing of protists on (13)C-labeled prey bacteria was developed which enables mass balances of the carbon turnover to be drawn, including yield estimation. Model experiments for validating the approach were performed in closed microcosms with the ciliate Uronema sp. and (13)C-labeled Escherichia coli as model prey. The transfer of bacterial (13)C into grazing protist biomass was investigated by fatty acid (FA) and RNA stable isotope probing (SIP). Uronema sp. showed ingestion rates of ∼390 bacteria protist(-1) h(-1), and the temporal patterns of (13)C assimilation from the prey bacteria to the protist FA were identified. Nine fatty acids specific for Uronema sp. were found (20:0, i20:0, 22:0, 24:0, 20:1ω9c, 20:1ω9t, 22:1ω9c, 22:1ω9t, and 24:1). Four of these fatty acids (22:0, 20:1ω9t, 22:1ω9c, and 22:1ω9t) were enriched very rapidly after 3 h, indicating grazing on bacteria without concomitant cell division. Other fatty acids (20:0, i20:0, and 20:1ω9c) were found to be indicative of growth with cell division. The fatty acids were found to be labeled with a percentage of labeled carbon (atoms percent [atom%]) up to 50. Eighteen percent of the E. coli-derived (13)C was incorporated into Uronema biomass, whereas 11% was mineralized. Around 5 mol bacterial carbon was necessary in order to produce 1 mol protist carbon (y(x)(/)(s) ≈ 0.2), and the temporal pattern of (13)C labeling of protist rRNA was also shown. A consumption of around 1,000 prey bacteria (∼98 atom% (13)C) per protist cell appears to be sufficient to provide detectable amounts of label in the protist RNA. The large shift in the buoyant density fraction of (13)C-labeled protist RNA demonstrated a high incorporation of (13)C, and reverse transcription-real-time PCR (RT-qPCR) confirmed that protist rRNA increasingly dominated in the heavy RNA fraction.
去除潜在的致病细菌,例如在废水处理过程中,通过吸附、过滤、自然死亡、病毒裂解和原生动物吞噬来实现,但原生动物吞噬的实际贡献从未被定量评估过。本文开发了一种系统的方法来分析原生动物对(13)C 标记猎物细菌的吞噬作用,该方法能够得出碳转化的质量平衡,包括产率估计。通过用纤毛虫 Uronema sp. 和(13)C 标记的大肠杆菌作为模型猎物进行验证实验,验证了该方法的有效性。通过脂肪酸(FA)和 RNA 稳定同位素探测(SIP)研究了细菌(13)C 转移到吞噬原生动物生物量中。Uronema sp. 的吞噬率约为 390 个细菌原生动物(-1)h(-1),并确定了从猎物细菌到原生动物 FA 的(13)C 同化的时间模式。发现了 9 种特定于 Uronema sp. 的脂肪酸(20:0、i20:0、22:0、24:0、20:1ω9c、20:1ω9t、22:1ω9c、22:1ω9t 和 24:1)。其中四种脂肪酸(22:0、20:1ω9t、22:1ω9c 和 22:1ω9t)在 3 小时后迅速富集,表明在没有伴随细胞分裂的情况下吞噬细菌。其他脂肪酸(20:0、i20:0 和 20:1ω9c)被发现是有细胞分裂的生长指示物。这些脂肪酸的标记碳百分比(原子百分比 [atom%])高达 50。约 18%的大肠杆菌衍生的(13)C 被整合到 Uronema 生物量中,而 11%被矿化。为了产生 1 摩尔原生动物碳,大约需要 5 摩尔细菌碳(y(x)(/)(s) ≈ 0.2),并且还显示了原生动物 rRNA 的(13)C 标记的时间模式。每个原生动物细胞似乎需要消耗约 1000 个猎物细菌(约 98 atom%(13)C),以在原生动物 RNA 中提供可检测量的标记。(13)C 标记的原生动物 RNA 的浮力密度分数的大幅变化表明了(13)C 的高掺入,逆转录实时 PCR(RT-qPCR)证实了原生动物 rRNA 越来越主导重 RNA 部分。