Department of Environmental Sciences, College of Life Sciences, Kuwait University, P.O. Box 5969, Safat 13060, Kuwait.
Department of Environmental Sciences, College of Life Sciences, Kuwait University, P.O. Box 5969, Safat 13060, Kuwait.
J Hazard Mater. 2024 May 15;470:134125. doi: 10.1016/j.jhazmat.2024.134125. Epub 2024 Mar 29.
The study addressed the challenge of treating petroleum industry wastewater with high concentrations of 1,2-dichloroethane (1,2-DCA) ranging from 384 to 1654 mg/L, which poses a challenge for bacterial biodegradation and algal photodegradation. To overcome this, a collaborative approach using membrane bioreactors (MBRs) that combine algae and bacteria was employed. This synergistic method effectively mitigated the toxicity of 1,2-DCA and curbed MBR fouling. Two types of MBRs were tested: one (B-MBR) used bacterial cultures and the other (AB-MBR) incorporated a mix of algal and bacterial cultures. The AB-MBR significantly contributed to 1,2-DCA removal, with algae accounting for over 20% and bacteria for approximately 49.5% of the dechlorination process. 1,2-DCA metabolites, including 2-chloroethanol, 2-chloro-acetaldehyde, 2-chloroacetic acid, and acetic acid, were partially consumed as carbon sources by algae. Operational efficiency peaked at a 12-hour hydraulic retention time (HRT) in AB-MBR, enhancing enzyme activities crucial for 1,2-DCA degradation such as dehydrogenase (DH), alcohol dehydrogenase (ADH), and acetaldehyde dehydrogenase (ALDH). The microbial diversity in AB-MBR surpassed that in B-MBR, with a notable increase in Proteobacteria, Bacteroidota, Planctomycetota, and Verrucomicrobiota. Furthermore, AB-MBR showed a significant rise in the dominance of 1,2-DCA-degrading genus such as Pseudomonas and Acinetobacter. Additionally, algal-degrading phyla (e.g., Nematoda, Rotifera, and Streptophyta) were more prevalent in AB-MBR, substantially reducing the issue of membrane fouling.
该研究解决了石油工业废水处理的难题,这些废水的 1,2-二氯乙烷(1,2-DCA)浓度高达 384 至 1654mg/L,这对细菌生物降解和藻类光降解都构成了挑战。为了克服这一难题,采用了一种联合膜生物反应器(MBR)的方法,该方法将藻类和细菌结合在一起。这种协同方法有效地减轻了 1,2-DCA 的毒性,并抑制了 MBR 的污垢形成。研究测试了两种类型的 MBR:一种(B-MBR)使用细菌培养物,另一种(AB-MBR)则结合了藻类和细菌的混合物。AB-MBR 对 1,2-DCA 的去除贡献显著,其中藻类占脱氯过程的 20%以上,细菌约占 49.5%。1,2-DCA 的代谢物,包括 2-氯乙醇、2-氯乙醛、2-氯乙酸和乙酸,部分被藻类用作碳源消耗。在 AB-MBR 中,水力停留时间(HRT)为 12 小时时达到最佳运行效率,提高了 1,2-DCA 降解所需的关键酶活性,如脱氢酶(DH)、醇脱氢酶(ADH)和乙醛脱氢酶(ALDH)。AB-MBR 中的微生物多样性超过了 B-MBR,其中变形菌门、拟杆菌门、浮霉菌门和疣微菌门的丰度显著增加。此外,AB-MBR 中 1,2-DCA 降解菌属(如假单胞菌属和不动杆菌属)的优势度显著增加。此外,藻类降解门(如线虫、轮虫和石松植物门)在 AB-MBR 中更为普遍,这大大减少了膜污染的问题。