不同前置缺氧池生物膜膜生物反应器处理海水养殖废水过程中的膜污染缓解。
Membrane fouling mitigation in different biofilm membrane bioreactors with pre-anoxic tanks for treating mariculture wastewater.
机构信息
Ningbo Institute of Technology, Zhejiang University, Ningbo 315000, China; Polytechnic Institute, Zhejiang University, Hangzhou 310000, China; Ningbo Key Laboratory of Urban and Rural Water Pollution Control Technology, Ningbo 315100, China.
Ningbo Institute of Technology, Zhejiang University, Ningbo 315000, China; Ningbo Research Institute, Zhejiang University, Ningbo 315100, China; Ningbo Key Laboratory of Urban and Rural Water Pollution Control Technology, Ningbo 315100, China.
出版信息
Sci Total Environ. 2020 Jul 1;724:138311. doi: 10.1016/j.scitotenv.2020.138311. Epub 2020 Mar 30.
This study compared the membrane fouling mitigation in two novel types of biofilm membrane bioreactor coupled with a pre-anoxic tank (BF-AO-MBR)-namely a fixed biofilm membrane bioreactor (FB-MBR) with fiber bundle bio-carriers and a moving-bed biofilm membrane bioreactor (MB-MBR) with suspended bio-carriers-relative to an anoxic/oxic MBR (AO-MBR), at salinities ranging from zero to 60 g/L. The results showed that the FB-MBR mitigated membrane fouling to a greater degree than the MB-MBR and AO-MBR. During operation, the FB-MBR exhibited the lowest fouling development, with three membrane filtration cycles, while the AO-MBR and MB-MBR had 22 and nine cycles, respectively. The key fouling factor in all reactors was cake layer resistance (R), which contributed to 89.61, 62.20, and 83.17% of the total fouling resistance (R) in AO-MBR, FB-MBR and MB-MBR, respectively. Additionally, in the FB-MBR, the pore blocking resistance (30.07%) was also an important cause of fouling. Fiber bundle bio-carriers and suspended bio-carriers reduced the R by 37.68% and 21.24% (mainly the R) compared to that of AO-MBR. Furthermore, FB-MBR and MB-MBR caused a decrease of suspended biomass (80.14 and 15.90%, respectively), and the latter exhibited a higher sludge particle size than AO-MBR, possibly resulting in the cake layer decline. The studied BF-AO-MBRs further alleviated the fouling propensity by reducing the amount of soluble microbial product (SMP) and extracellular polymeric substances (EPS) under all salinity levels, especially the FB-MBR. Among the protein components, the amounts of tryptophan protein-like substance and aromatic protein-like substance were significantly lower in the FB-MBR compared to the AO-MBR and MB-MBR. Additionally, at 60 g/L salinity, the structure of the microbial community in the FB-MBR had a lower abundance of Bacteroidetes and more biomacromolecule degraders, which may have contributed to the moderation of membrane fouling.
本研究比较了两种新型生物膜膜生物反应器(BF-AO-MBR)——即带有纤维束生物载体的固定生物膜膜生物反应器(FB-MBR)和带有悬浮生物载体的移动床生物膜膜生物反应器(MB-MBR)——与缺氧/好氧膜生物反应器(AO-MBR)在零到 60g/L 盐度下减轻膜污染的效果。结果表明,FB-MBR 比 MB-MBR 和 AO-MBR 更能减轻膜污染。在运行过程中,FB-MBR 表现出最低的污染发展,经过三个膜过滤周期,而 AO-MBR 和 MB-MBR 分别为 22 个和 9 个周期。所有反应器中的关键污染因素是滤饼阻力(R),其在 AO-MBR、FB-MBR 和 MB-MBR 中的总污染阻力(R)中分别占 89.61%、62.20%和 83.17%。此外,在 FB-MBR 中,孔堵塞阻力(30.07%)也是污染的一个重要原因。纤维束生物载体和悬浮生物载体比 AO-MBR 分别减少了 37.68%和 21.24%的 R(主要是 R)。此外,FB-MBR 和 MB-MBR 导致悬浮生物量减少(分别为 80.14%和 15.90%),后者的污泥粒径比 AO-MBR 高,可能导致滤饼下降。在所有盐度水平下,研究的 BF-AO-MBR 通过减少可溶性微生物产物(SMP)和细胞外聚合物(EPS)的量进一步减轻了污染倾向,尤其是 FB-MBR。在蛋白质成分中,与 AO-MBR 和 MB-MBR 相比,FB-MBR 中色氨酸蛋白样物质和芳香族蛋白样物质的含量明显降低。此外,在 60g/L 盐度下,FB-MBR 中微生物群落的结构中,拟杆菌门的丰度较低,生物大分子降解菌较多,这可能有助于减轻膜污染。