Pembroke J Tony, Ryan Michael P
Department of Chemical Sciences, School of Natural Sciences and Bernal Institute, University of Limerick, V94 T9PX Limerick, Ireland.
Microorganisms. 2019 Jul 25;7(8):215. doi: 10.3390/microorganisms7080215.
Autothermal thermophilic aerobic digestion (ATAD) is a microbial fermentation process characterized as a tertiary treatment of waste material carried out in jacketed reactors. The process can be carried out on a variety of waste sludge ranging from human, animal, food, or pharmaceutical waste where the addition of air initiates aerobic digestion of the secondary treated sludge material. Digestion of the sludge substrates generates heat, which is retained within the reactor resulting in elevation of the reactor temperature to 70-75 °C. During the process, deamination of proteinaceous materials also occurs resulting in liberation of ammonia and elevation of pH to typically pH 8.4. These conditions result in a unique microbial consortium, which undergoes considerable dynamic change during the heat-up and holding phases. The change in pH and substrate as digestion occurs also contributes to this dynamic change. Because the large reactors are not optimized for aeration, and because low oxygen solubility at elevated temperatures occurs, there are considerable numbers of anaerobes recovered which also contributes to the overall digestion. As the reactors are operated in a semi-continuous mode, the reactors are rarely washed, resulting in considerable biofilm formation. Equally, because of the fibrous nature of the sludge, fiber adhering organisms are frequently found which play a major role in the overall digestion process. Here, we review molecular tools needed to examine the ATAD sludge consortia, what has been determined through phylogenetic analysis of the consortia and the nature of the dynamics occurring within this unique fermentation environment.
自热嗜热需氧消化(ATAD)是一种微生物发酵过程,其特点是在夹套式反应器中对废料进行三级处理。该过程可在各种废污泥上进行,这些废污泥包括人类、动物、食品或制药废料,其中通入空气可启动对二次处理污泥材料的需氧消化。污泥底物的消化产生热量,热量保留在反应器内,导致反应器温度升高至70-75°C。在这个过程中,蛋白质材料也会发生脱氨反应,导致氨的释放和pH值升高至通常为8.4。这些条件导致形成独特的微生物群落,该群落在升温阶段和保温阶段会发生相当大的动态变化。消化过程中pH值和底物的变化也促成了这种动态变化。由于大型反应器未针对曝气进行优化,且高温下氧气溶解度较低,因此回收了大量厌氧菌,这也有助于整体消化。由于反应器以半连续模式运行,很少进行清洗,导致形成大量生物膜。同样,由于污泥的纤维性质,经常会发现附着纤维的生物体,它们在整个消化过程中起着重要作用。在这里,我们回顾了研究ATAD污泥群落所需的分子工具,通过对群落的系统发育分析确定了什么,以及在这种独特的发酵环境中发生的动态变化的性质。