Li Chun-Teh, Lee Wen-Jhy, Huang Kuo-Lin, Fu Sheng-Feng, Lait Yi-Chieh
Department of Environmental Engineering, National Cheng Kung University, Tainan 70101, Taiwan.
Environ Sci Technol. 2007 Apr 15;41(8):2950-6. doi: 10.1021/es062803d.
This work investigated the vitrification of hazardous electroplating sludge containing 140 mg/g Cr with/without bottom ash or cullet conditioning to lower specimens' basicities to 0.97-1.17 or 0.18-0.23, respectively. The conditioning was found to enhance the smooth/glassy appearance of slags but no ingot was obtained. Cr was >98% retained in the vitrified slags. Cr2O3 dominated in crystalline structure for the slag vitrified from the sludge, but this domination gradually shifted to Fe2SiO4/Fe3O4/SiO2 or SiO2 crystalline with increasing addition of bottom ash or cullet into the sludge, respectively. Compared to the raw sludge, the sludge-vitrified slag displayed lower leaching concentrations for most metals (particularly Cr (2.54 mg/L)), and smaller leaching ratios for Ag, Cr, and Cu (1.35, 0.02, and <0.01%, respectively) but greater ones for Cd, Pb, and Zn (3.83, 2.46, and 0.36%, respectively). The Cr leaching ratios were approximately 0.01% for the slags vitrified from the conditioned sludge. Independent of the slag basicity and crystalline structure, metal leaching quantity increased but leaching ratio decreased with increasing slag metal content. The slag compressive strengths were improved to >14.7 MPa at the mixing ratios > or = 2/1 and 1/1 for bottom ash/sludge and cullet/sludge, respectively. Fulfilling the criteria of Toxicity Characteristic Leaching Procedure (TCLP), all the slags were recyclable.
本研究探讨了含铬量为140 mg/g的危险电镀污泥的玻璃化处理,分别添加或不添加底灰或碎玻璃进行调质,以使样品碱度分别降至0.97 - 1.17或0.18 - 0.23。结果发现,调质处理可增强炉渣的光滑/玻璃状外观,但未获得铸锭。铬在玻璃化炉渣中的保留率>98%。对于由污泥玻璃化得到的炉渣,Cr2O3在晶体结构中占主导地位,但随着向污泥中分别增加底灰或碎玻璃的添加量,这种主导地位逐渐分别转变为Fe2SiO4/Fe3O4/SiO2或SiO2晶体。与原始污泥相比,污泥玻璃化炉渣对大多数金属的浸出浓度较低(特别是铬(2.54 mg/L)),银、铬和铜的浸出率较小(分别为1.35%、%和<0.01%),但镉、铅和锌的浸出率较大(分别为3.83%、2.46%和0.36%)。经调质污泥玻璃化得到的炉渣中铬的浸出率约为0.01%。与炉渣碱度和晶体结构无关,随着炉渣金属含量的增加,金属浸出量增加但浸出率降低。对于底灰/污泥和碎玻璃/污泥的混合比例分别≥2/1和1/1时,炉渣抗压强度提高到>14.7 MPa。所有炉渣均符合毒性特性浸出程序(TCLP)标准,可回收利用。