Drogui Patrick, Blais Jean-François, Mercier Guy
INRS-ETE, Quebéc, Canada.
Water Environ Res. 2005 Jul-Aug;77(4):372-80. doi: 10.2175/106143005x51950.
Bioleaching processes have been demonstrated to be effective technologies in removing heavy metals from wastewater sludge, but long hydraulic retention times are typically required to operate these bioprocesses. A hybrid process (coupling biological and chemical processes) has been explored in laboratory pilot-scale experiments for heavy metals (cadmium [Cd], copper [Cu], chromium [Cr], and zinc [Zn]) removal from three types of sludge (primary sludge, secondary activated sludge, and a mixture of primary and secondary sludge). The hybrid process consisted of producing a concentrate ferric ion solution followed by chemical treatment of sludges. Ferric iron solution was produced biologically via oxidation of ferrous iron by A. ferrooxidans in a continuous-flow stirred tank (5.2 L) reactor (CSTR). Wastewater sludge filtrate (WSF) containing nutrients (phosphorus and nitrogen) has been used as culture media to support the growth and activity of indigenous iron-oxidizing bacteria. Results showed that total organic carbon (TOC) concentrations of the culture media in excess of 235 mg/L were found to be inhibitory to bacterial growth. The oxidation rate increased as ferrous iron concentrations ranged from 10 to 40 g Fe2+/L. The percentage of ferrous iron (Fe2+) oxidized to ferric iron (Fe3+) increased as the hydraulic retention time (HRT) increased from 12 to 48 h. Successful and complete Fe2+ oxidation was recorded at a HRT of 48 h using 10 g Fe2+/L. Subsequently, ferric ion solution produced by A. ferrooxidans in sludge filtrate was used to solubilize heavy metals contained in wastewater sludge. The best solubilization was obtained with a mixture of primary and secondary sludge, demonstrating a removal efficiency of 63, 71, 49, and 80% for Cd, Cu, Cr, and Zn, respectively.
生物浸出工艺已被证明是从废水污泥中去除重金属的有效技术,但运行这些生物工艺通常需要较长的水力停留时间。在实验室中试规模实验中,探索了一种混合工艺(生物和化学工艺相结合)用于从三种类型的污泥(初沉污泥、二级活性污泥以及初沉污泥与二级活性污泥的混合物)中去除重金属(镉[Cd]、铜[Cu]、铬[Cr]和锌[Zn])。该混合工艺包括制备浓缩铁离子溶液,随后对污泥进行化学处理。铁离子溶液通过在连续流搅拌槽(5.2升)反应器(CSTR)中,由氧化亚铁硫杆菌将亚铁离子氧化而生物制备。含有营养物质(磷和氮)的废水污泥滤液(WSF)已被用作培养基,以支持本地铁氧化细菌的生长和活性。结果表明,培养基中总有机碳(TOC)浓度超过235毫克/升被发现对细菌生长有抑制作用。随着亚铁离子浓度在10至40克Fe2+/升范围内变化,氧化速率增加。当水力停留时间(HRT)从12小时增加到48小时时,亚铁离子(Fe2+)氧化为铁离子(Fe3+)的百分比增加。在HRT为48小时、亚铁离子浓度为10克Fe2+/升时,记录到亚铁离子成功且完全氧化。随后,氧化亚铁硫杆菌在污泥滤液中产生的铁离子溶液被用于溶解废水污泥中所含重金属。初沉污泥与二级活性污泥的混合物获得了最佳的溶解效果,镉、铜、铬和锌的去除效率分别为63%、71%、49%和80%。