Department of Civil and Environmental Engineering, Water Technology Center, Chinese National Engineering Research Center for Control & Treatment of Heavy Metal Pollution (Hong Kong Branch), The Hong Kong University of Science and Technology, Hong Kong China; Shenzhen Research Institute, Fok Ying Tung Graduate School, The Hong Kong University of Science and Technology, Guangdong, China.
Department of Civil and Environmental Engineering, Water Technology Center, Chinese National Engineering Research Center for Control & Treatment of Heavy Metal Pollution (Hong Kong Branch), The Hong Kong University of Science and Technology, Hong Kong China.
Water Res. 2019 Dec 1;166:115038. doi: 10.1016/j.watres.2019.115038. Epub 2019 Sep 5.
Sulfide-oxidizing autotrophic denitrification (SOAD) implemented in a moving-bed biofilm reactor (MBBR) is a promising alternative to conventional heterotrophic denitrification in mainstream biological nitrogen removal. The sulfide-oxidation intermediate - elemental sulfur - is crucial for the kinetic and microbial properties of the sulfur-oxidizing bacterial communities, but its role is yet to be studied in depth. Hence, to investigate the performance and microbial communities of the aforementioned new biosystem, we operated for a long term a laboratory-scale (700 d) SOAD MBBR to treat synthetic saline domestic sewage, with an increase of the surface loading rate from 8 to 50 mg N/(m·h) achieved by shortening the hydraulic retention time from 12 h to 2 h. The specific reaction rates of the reactor were eventually increased up to 0.37 kg N/(m·d) and 0.73 kg S/(m·d) for nitrate reduction and sulfide oxidation with no significant sulfur elemental accumulation. Two sulfur-oxidizing bacterial (SOB) clades, Sox-independent SOB (SOB) and Sox-dependent SOB (SOB), were responsible for indirect two-step sulfur oxidation (S→S→SO) and direct one-step sulfur oxidation (S→SO), respectively. The SOB biomass-specific electron transfer capacity could be around 2.5 times greater than that of SOB (38 mmol e/(gSOB·d) versus 15 mmol e/(gSOB·d)), possibly resulting in the selection of SOB over SOB under stress conditions (such as a shorter HRT). Further studies on the methods and mechanism of selecting of SOB over SOB in biofilm reactors are recommended. Overall, the findings shed light on the design and operation of MBBR-based SOAD processes for mainstream biological denitrification.
在移动床生物膜反应器(MBBR)中实施的硫自养反硝化(SOAD)是传统主流生物脱氮中异养反硝化的一种很有前途的替代方法。硫氧化中间产物-元素硫-对硫氧化细菌群落的动力学和微生物特性至关重要,但它的作用尚未得到深入研究。因此,为了研究上述新型生物系统的性能和微生物群落,我们在实验室规模(700 天)的 SOAD MBBR 中进行了长期运行,以处理合成盐水生活污水,通过将水力停留时间从 12 小时缩短至 2 小时,将表面负荷率从 8mg N/(m·h)提高到 50mg N/(m·h)。反应器的比反应速率最终提高到 0.37kg N/(m·d)和 0.73kg S/(m·d),用于硝酸盐还原和硫化物氧化,而没有明显的元素硫积累。两个硫氧化细菌(SOB)类群,硫代依赖型 SOB(SOB)和硫代非依赖型 SOB(SOB),分别负责间接两步硫氧化(S→S→SO)和直接一步硫氧化(S→SO)。SOB 生物量比电子传递能力可能比 SOB 高 2.5 倍(38mmol e/(gSOB·d)对 15mmol e/(gSOB·d)),这可能导致在应激条件下(如较短的 HRT)选择 SOB 而不是 SOB。建议进一步研究生物膜反应器中选择 SOB 而不是 SOB 的方法和机制。总的来说,这些发现为基于 MBBR 的主流生物脱氮 SOAD 工艺的设计和运行提供了启示。