Gu X Y, Wong J W C
Department of Biology, Hong Kong Baptist University, Kowloon Tong, Hong Kong SAR, P.R. China.
Environ Technol. 2004 Aug;25(8):889-97. doi: 10.1080/09593330.2004.9619382.
The objective of the present study was to isolate the indigenous iron-oxidizing bacterium and compare its effectiveness in bioleaching of heavy metals from fresh anaerobically digested sludge and aged sludge which had undergone a storage period in a sludge holding tank. An acidophilic iron-oxidizing bacterium Acidithiobacillus ferrooxidans strain ANYL-1 was successfully isolated from the sludge collected from a wastewater treatment plant at Yuen Long district in Hong Kong. It was a Gram negative, non-motile rod shaped bacterium which used ferrous iron, elemental sulfur or thiosulfate as energy source, but did not utilize tetrathionate or glucose as energy source. The optimal temperature and pH for its growth and iron oxidation were 30-35 degrees C and pH 2.0-2.5, respectively. When it was used in the bioleaching of anaerobically digested sewage sludge, an inhibition on metal solubilization was observed in fresh sludge except for Zn whose dissolution was solely a chemical process. Compared to the 3 and 4 days required for solubilization of Cu and Cr respectively from the sludge sample collected after the sludge holding tank (Sludge SHT), 6 days were required to bioleach Cu and Cr from fresh sludge (Sludge AD). The fresh sewage sludge posed an unfavorable condition for bioleaching of heavy metals from anaerobically digested sludge as reflected by the prolonged bioleaching time. Therefore, further studies were needed to understand the inhibitory effects in the fresh anaerobically digested sludge and develop measures to remove it in order to improve the heavy metal bioleaching efficiency.
本研究的目的是分离本地铁氧化细菌,并比较其从新鲜厌氧消化污泥和在污泥储存池中经过储存期的老化污泥中生物浸出重金属的效果。从香港元朗区一家污水处理厂收集的污泥中成功分离出一株嗜酸铁氧化细菌氧化亚铁硫杆菌ANYL-1菌株。它是革兰氏阴性、无运动性的杆状细菌,以亚铁离子、单质硫或硫代硫酸盐作为能源,但不利用连四硫酸盐或葡萄糖作为能源。其生长和铁氧化的最佳温度和pH分别为30-35℃和pH 2.0-2.5。当它用于厌氧消化污水污泥的生物浸出时,除了锌的溶解完全是一个化学过程外,在新鲜污泥中观察到对金属溶解的抑制作用。与从污泥储存池(污泥SHT)后收集的污泥样品中分别溶解铜和铬所需的3天和4天相比,从新鲜污泥(污泥AD)中生物浸出铜和铬需要6天。新鲜污水污泥对厌氧消化污泥中重金属的生物浸出构成不利条件,这一点从延长的生物浸出时间可以看出。因此,需要进一步研究以了解新鲜厌氧消化污泥中的抑制作用,并制定去除措施,以提高重金属生物浸出效率。