Department of Civil and Environmental Engineering, Chinese National Engineering Research Center for Control & Treatment of Heavy Metal Pollution (Hong Kong Branch), and Water Technology Center, The Hong Kong University of Science and Technology, Hong Kong, China.
Department of Civil and Environmental Engineering, Chinese National Engineering Research Center for Control & Treatment of Heavy Metal Pollution (Hong Kong Branch), and Water Technology Center, The Hong Kong University of Science and Technology, Hong Kong, China; Wastewater Treatment Laboratory, FYT Graduate School, and Shenzhen Institute, The Hong Kong University of Science and Technology, Guangdong, China.
Water Res. 2019 Mar 15;151:44-53. doi: 10.1016/j.watres.2018.12.008. Epub 2018 Dec 15.
In biological wastewater treatment, the bacteria starvation always challenges the stability of system operation. Yet, the effects of starvation and possibility of reactivation are less understood for anaerobic sulfidogenic system. Sulfidogenic systems use sulfate as electron acceptor for organic chemical oxygen demand (COD) degradation, so it will encounter two kind of starvations: (i) complete stoppage of wastewater flow (named complete food starvation) and (ii) remaining organic COD but with very low level sulfate in the influent (named sulfate starvation). In this study, the relative long-term starvation (over 30-day) and subsequent reactivation were studied in two lab-scale continuous gas recirculation sulfate-reducing upflow sludge bed (CGR-SRUSB) reactors. It was observed that the complete food starvation and sulfate starvation decreased the COD removal rate (in the similar range of 60-65%) and the specific sulfidogenic activity (about 45% and 61% respectively), as well as increasing the sludge flotation potential (SFP) from <15% to 58% and 35% respectively. Moreover, the following restoration experiments proved that the perturbed systems could be reactivated within 10-15 days for both cases. The results of investigating the mechanisms showed the performance deterioration were highly attributed to the starvation-induced granular sludge transitions, with respect to the changing of sludge physico-chemical properties (permeability, porosity, hydrophobicity and viscocity) and microbial stuctures (sulfate-reducting bacteria and extracellular polymeric substances). The outcomes of this study can provide useful information for dealing with the prolonged starvation problems in sulfidogenesis-based systems in industrial and municipal wastewater treatment.
在生物废水处理中,细菌饥饿总是对系统运行的稳定性构成挑战。然而,对于厌氧硫酸盐还原系统,饥饿的影响和再激活的可能性还不太了解。硫酸盐还原系统利用硫酸盐作为电子受体来降解有机化学需氧量(COD),因此它会遇到两种饥饿状态:(i)完全停止废水流动(称为完全食物饥饿)和(ii)进水有机 COD 仍然存在,但硫酸盐水平非常低(称为硫酸盐饥饿)。在这项研究中,在两个实验室规模的连续气体循环硫酸盐还原上流式污泥床(CGR-SRUSB)反应器中研究了相对长期的饥饿(超过 30 天)和随后的再激活。结果表明,完全食物饥饿和硫酸盐饥饿都会降低 COD 去除率(在相似的 60-65%范围内)和特定的硫酸盐还原活性(分别约为 45%和 61%),并分别将污泥浮选潜力(SFP)从<15%增加到 58%和 35%。此外,后续的恢复实验证明,对于两种情况,受干扰的系统都可以在 10-15 天内得到恢复。对机制的研究结果表明,性能恶化主要归因于饥饿诱导的颗粒污泥转变,与污泥物理化学性质(渗透性、孔隙率、疏水性和粘性)和微生物结构(硫酸盐还原菌和胞外聚合物)的变化有关。本研究的结果可为处理工业和城市废水处理中基于硫酸盐还原的系统中长时间饥饿问题提供有用信息。