Weber S D, Ludwig W, Schleifer K-H, Fried J
Lehrstuhl für Mikrobiologie, Technische Universität München, Am Hochanger 4, 85350 Freising, Germany.
Appl Environ Microbiol. 2007 Oct;73(19):6233-40. doi: 10.1128/AEM.01002-07. Epub 2007 Aug 17.
Aerobic activated sludge granules are dense, spherical biofilms which can strongly improve purification efficiency and sludge settling in wastewater treatment processes. In this study, the structure and development of different granule types were analyzed. Biofilm samples originated from lab-scale sequencing batch reactors which were operated with malthouse, brewery, and artificial wastewater. Scanning electron microscopy, light microscopy, and confocal laser scanning microscopy together with fluorescence in situ hybridization (FISH) allowed insights into the structure of these biofilms. Microscopic observation revealed that granules consist of bacteria, extracellular polymeric substances (EPS), protozoa and, in some cases, fungi. The biofilm development, starting from an activated sludge floc up to a mature granule, follows three phases. During phase 1, stalked ciliated protozoa of the subclass Peritrichia, e.g., Epistylis spp., settle on activated sludge flocs and build tree-like colonies. The stalks are subsequently colonized by bacteria. During phase 2, the ciliates become completely overgrown by bacteria and die. Thereby, the cellular remnants of ciliates act like a backbone for granule formation. During phase 3, smooth, compact granules are formed which serve as a new substratum for unstalked ciliate swarmers settling on granule surfaces. These mature granules comprise a dense core zone containing bacterial cells and EPS and a loosely structured fringe zone consisting of either ciliates and bacteria or fungi and bacteria. Since granules can grow to a size of up to several millimeters in diameter, we developed and applied a modified FISH protocol for the study of cryosectioned biofilms. This protocol allows the simultaneous detection of bacteria, ciliates, and fungi in and on granules.
好氧活性污泥颗粒是致密的球形生物膜,在废水处理过程中能显著提高净化效率和污泥沉降性能。在本研究中,分析了不同颗粒类型的结构和发育情况。生物膜样本取自实验室规模的序批式反应器,这些反应器采用麦芽厂、啤酒厂和人工废水进行运行。扫描电子显微镜、光学显微镜、共聚焦激光扫描显微镜以及荧光原位杂交技术(FISH)使我们能够深入了解这些生物膜的结构。显微镜观察表明,颗粒由细菌、胞外聚合物(EPS)、原生动物以及某些情况下的真菌组成。生物膜的发育过程,从活性污泥絮体开始直至成熟颗粒,可分为三个阶段。在第一阶段,缘毛亚纲的柄纤毛虫,例如累枝虫属(Epistylis spp.),附着在活性污泥絮体上并形成树状菌落。随后,细菌在柄上定殖。在第二阶段,纤毛虫完全被细菌覆盖并死亡。因此,纤毛虫的细胞残骸成为颗粒形成的骨架。在第三阶段,形成光滑、致密的颗粒,这些颗粒成为未具柄的纤毛虫游动体附着在颗粒表面的新基质。这些成熟颗粒包括一个含有细菌细胞和EPS的致密核心区以及一个由纤毛虫和细菌或真菌和细菌组成的结构松散的边缘区。由于颗粒直径可生长至数毫米,我们开发并应用了一种改进的FISH方案来研究冷冻切片生物膜。该方案能够同时检测颗粒内部和表面的细菌、纤毛虫和真菌。