College of Environmental and Resource Sciences , Zhejiang University , Hangzhou , China 310058.
Advanced Water Management Centre , The University of Queensland , St. Lucia , Queensland 4072 , Australia.
Environ Sci Technol. 2018 Sep 18;52(18):10680-10688. doi: 10.1021/acs.est.8b02374. Epub 2018 Aug 27.
For the first time, we demonstrated vanadate (V(V)) reduction in a membrane biofilm reactor (MBfR) using CH as the sole electron donor. The V(V)-reducing capability of the biofilm kept increasing, with complete removal of V(V) achieved when the influent surface loading of V(V) was 363 mg m day. Almost all V(V) was reduced to V(IV) precipitates, which is confirmed by a scanning electron microscope coupled to energy dispersive X-ray spectroscopy (SEM-EDS) and X-ray photoelectron spectroscopy (XPS). Microbial community analysis revealed that denitrifiers Methylomonas and Denitratisoma might be the main genera responsible for V(V) reduction. The constant enrichment of Methylophilus suggests that the intermediate (i.e., methanol) from CH metabolism might be used as the electron carriers for V(V) bioreduction. Intrusion of V(V) (2-5 mg/L, at the surface loading of 150-378 mg m day) into the biofilm stimulated the secretion of extracellular polymeric substances (EPS), but high loading of V(V) (10 mg/L, at the surface loading of 668 mg m day) decreased the amount of EPS. Metagenomic prediction analysis established the strong correlation between the secretion of EPS and the microbial metabolism associated with V(V) reduction, tricarboxylic acid cycle (TCA) cycle, methane oxidation, and ATP production, and EPS might relieve the oxidative stress induced by high loading of V(V). Colorimetric determination and a three-dimensional excitation-emission matrix (3D-EEM) showed that tryptophan and humic acid-like substances might play important roles in microbial cell protection and V(V) binding. Fourier transform infrared (FTIR) spectroscopy identified hydroxyl (-OH) and carboxyl (COO) groups in EPS as the candidate functional groups for binding V(V).
我们首次在膜生物膜反应器(MBfR)中使用 CH 作为唯一电子供体证明了偏钒酸盐(V(V))的还原。生物膜的 V(V)还原能力不断增加,当 V(V)的入口表面负荷为 363 mg m day 时,V(V)完全去除。几乎所有的 V(V)都被还原为 V(IV)沉淀物,这一点通过扫描电子显微镜与能量色散 X 射线光谱(SEM-EDS)和 X 射线光电子能谱(XPS)相结合得到证实。微生物群落分析表明,反硝化菌 Methylomonas 和 Denitratisoma 可能是主要负责 V(V)还原的属。Methylophilus 的不断富集表明,CH 代谢的中间产物(即甲醇)可能被用作 V(V)生物还原的电子载体。生物膜中 V(V)(2-5mg/L,表面负荷为 150-378mg m day)的侵入刺激了细胞外聚合物物质(EPS)的分泌,但 V(V)的高负荷(10mg/L,表面负荷为 668mg m day)降低了 EPS 的量。宏基因组预测分析建立了 EPS 分泌与与 V(V)还原、三羧酸循环(TCA)循环、甲烷氧化和 ATP 产生相关的微生物代谢之间的强相关性,EPS 可能缓解高负荷 V(V)引起的氧化应激。比色测定和三维激发发射矩阵(3D-EEM)表明色氨酸和腐殖酸类物质可能在微生物细胞保护和 V(V)结合中发挥重要作用。傅里叶变换红外(FTIR)光谱鉴定了 EPS 中的羟基(-OH)和羧基(COO)基团作为结合 V(V)的候选功能基团。