State Key Laboratory of Pollution Control and Resources Reuse, College of Environmental Science and Engineering, Tongji University, Siping Road, Shanghai 200092, PR China.
State Key Laboratory of Pollution Control and Resources Reuse, College of Environmental Science and Engineering, Tongji University, Siping Road, Shanghai 200092, PR China.
Water Res. 2015 Apr 15;73:252-64. doi: 10.1016/j.watres.2015.01.034. Epub 2015 Feb 7.
Industrial wastewater containing heavy metals that enters municipal wastewater treatment plants inevitably has a toxic impact on biological treatment processes. In this study, the impact of Cu(II) (0, 1.5, 2, 2.5, 3 mg/L) on the performance of denitrifying phosphorus removal (DPR) and microbial community structures was investigated. Particularly, the dynamic change in the amount and composition of extracellular polymeric substances (EPS), and the role of EPS in P removal, were assessed using three-dimensional excitation-emission matrix fluorescence spectroscopy combined with parallel factor (PARAFAC) analysis. The results showed that, after long-term adjustment, the P removal efficiency was maintained at 95 ± 2.7% at Cu(II) addition up to 2.5 mg/L, but deteriorated when the Cu(II) addition was 3 mg/L. The EPS content, including proteins and humic substances, increased with increasing Cu(II) additions at concentrations ≤2.5 mg/L. This property of EPS was beneficial for protecting phosphate-accumulating organisms (PAOs) against heavy metals, as both proteins and humic substances are strong ligands for Cu(II). Therefore, the PAOs abundance was still relatively high (67 ± 3%) when Cu(II) accumulation in sludge was up to 10 mg/g SS. PARAFAC confirmed that aromatic proteins could be transformed into soluble microbial byproduct-like material when microorganisms were subjected to Cu(II) stress, owing to their strong metal ion complexing capacity. The increase in the percentage of humic-like substances enhanced the detoxification function of the sludge EPS. EPS accounted for approximately 26-47% of P removed by adsorption when Cu(II) additions were between 0 and 2.5 mg/L. The EPS function, including binding toxic heavy metals and P storage, enhanced the operating stability of DPR systems. This study provides us with a better understanding of (1) the tolerance of DPR sludge to copper toxicity and (2) the function of sludge EPS in the presence of heavy metals in biological P removal systems.
含有重金属的工业废水进入城市污水处理厂,不可避免地会对生物处理过程产生毒性影响。本研究考察了 Cu(II)(0、1.5、2、2.5、3mg/L)对反硝化除磷(DPR)性能和微生物群落结构的影响。特别地,使用三维激发-发射矩阵荧光光谱法结合平行因子(PARAFAC)分析评估了胞外聚合物物质(EPS)的数量和组成的动态变化,以及 EPS 在 P 去除中的作用。结果表明,在长期调整后,当 Cu(II) 添加量高达 2.5mg/L 时,P 去除效率保持在 95±2.7%,但当 Cu(II) 添加量为 3mg/L 时则恶化。EPS 含量(包括蛋白质和腐殖质)随着 Cu(II)添加量的增加而增加,在浓度≤2.5mg/L 时增加。这种 EPS 的特性有利于保护聚磷菌(PAOs)免受重金属的影响,因为蛋白质和腐殖质都是 Cu(II)的强配体。因此,当污泥中 Cu(II)积累达到 10mg/g SS 时,PAOs 的丰度仍相对较高(67±3%)。PARAFAC 证实,当微生物受到 Cu(II)胁迫时,芳香族蛋白质可以转化为可溶性微生物副产物样物质,因为它们具有很强的金属离子络合能力。腐殖质样物质的比例增加增强了污泥 EPS 的解毒功能。当 Cu(II)添加量在 0 至 2.5mg/L 之间时,EPS 占通过吸附去除的 P 的 26-47%左右。EPS 的功能,包括结合有毒重金属和 P 储存,增强了 DPR 系统的运行稳定性。本研究使我们更好地了解(1)DPR 污泥对铜毒性的耐受性和(2)在生物 P 去除系统中存在重金属时污泥 EPS 的功能。