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Mechanism of toxicity formation and spatial distribution in activated sludge treating synthetic effluent containing bisphenol A (BPA)

机译:活性污泥处理含双酚A(BPA)的合成废水的毒性形成和空间分布机理

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Organic sludge toxicity is a critical issue for sludge land applications. To investigate sludge organic toxicity formation and spatial distribution properties, sludge was acclimated using synthetic effluent containing various bisphenol A (BPA) concentrations in sequential aerobic activated sludge reactors (SBRs). Acute sludge toxicity, which was characterized by the inhibition rate of the luminescent bacterium Photobacterium phosphoreum, was the focus of this study. The original influent COD of the SBR was approximately 300 mg/L; the sludge retention time (SRT) and hydraulic retention time (HRT) were controlled at 20 d and 12 h, respectively. The results indicated that a positive correlation existed between sludge toxicity and the influent BPA concentration. Furthermore, the toxicity was centralized in the intracellular and inner sections of extracellular polymeric substance (EPS) in sludge flocs. BPA concentrations were controlled at 2.5 mg/L, 5.0 mg/L, 7.5 mg/L and 20 mg/L; the sludge toxicities, measured by comparing the control SBR with the blank, were 2.99%, 4.05%, 6.99% and 10.64%, respectively, at the end of 28-day operation. In the 12-h SBR treatment process, aqueous and sludge phase BPA was completely removed within 2 h. However, the maximum sludge toxicity appeared in the 8th hour. The DGGE analysis suggested that the existence of BPA in wastewater increased bacterial diversity in activated sludge. However, the bacterial similarity between sludge in SBRs decreased with increasing BPA concentration. Lastly, the bacterial similarity between blank sludge and control sludge of 20 mg/L BPA was 0.47.
机译:有机污泥的毒性是污泥土地应用中的关键问题。为了研究污泥的有机毒性形成和空间分布特性,在顺序好氧活性污泥反应器(SBR)中使用含有各种双酚A(BPA)浓度的合成废水对污泥进行驯化。急性污泥毒性的特征是发光细菌磷细菌的抑制率,是本研究的重点。 SBR的原始进水COD约为300 mg / L;污泥停留时间(SRT)和水力停留时间(HRT)分别控制在20 d和12 h。结果表明,污泥毒性与进水BPA浓度呈正相关。此外,毒性集中在污泥絮体的细胞内和细胞外聚合物质(EPS)内部。 BPA浓度控制在2.5 mg / L,5.0 mg / L,7.5 mg / L和20 mg / L;在运行28天后,通过将对照SBR与空白进行比较,测得的污泥毒性分别为2.99%,4.05%,6.99%和10.64%。在12小时的SBR处理过程中,水相和污泥相BPA在2小时内被完全去除。但是,最大污泥毒性出现在第8小时。 DGGE分析表明,废水中BPA的存在增加了活性污泥中细菌的多样性。然而,SBRs污泥之间的细菌相似性随BPA浓度的增加而降低。最后,空白污泥和对照污泥的BPA 20 mg / L之间的细菌相似度为0.47。

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