Sang Yimin, Liang Zengyin, Li Chenyang, Lu Taotao, Zhu Ling, Sun Yiming, Gu Qingbao
Department of Environmental Engineering, Beijing Institute of Petrochemical Technology, Beijing, 102617, China.
State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing, 100012, China.
Environ Sci Pollut Res Int. 2022 Dec;29(56):85537-85546. doi: 10.1007/s11356-022-21803-9. Epub 2022 Jul 7.
Spent cathode carbon (SCC) is a hazardous waste containing fluorides and cyanides from aluminum electrolysis. Many literatures have focused on SCC leaching; however, SCC hazard-free treatment remains understudied. This article used 10.0 g raw SCC sample to explore the vitric/kaolin solidification and calcium stabilization of SCC, and analyze their hazard-free mechanisms by the methods of XRD and SEM. The leached fluorides were all below the Chinese identification standard for hazardous wastes (GB5085.3-2007), whether at 750/950 °C for 60 min above 8.0 g vitric, or at 1200 °C for 120 min with above 8.0 g kaolin, or above 700 °C for more than 30 min with above 0.5 g CaCO. Kaolin/vitric solidification relied on the massive addition of vitric and kaolin to produce glassy or glass-like material (KO·AlO·6SiO) which may retain fluoride. Calcium stabilization converted soluble fluoride NaF in raw SCC sample into insoluble CaF. Heating 60 min at 500-1200 °C at oxygen atmosphere decomposed almost of cyanides, with leached cyanides meeting Chinese standard GB5085.3-2007. Mass-loss rates of kaolin addition came from a large amount of adsorbed water and structural water in kaolinite and illite wai lost, and that of CaCO/CaSO addition was attributed to their decomposition into volatile CO/SO, while that of CaO was a little negative due to its absorption of water vapor and CO. In brief, as the effective hazard-free manner of SCC, both kaolin/vitric solidification and calcium stabilization successfully have achieved fluoride immobilization and cyanide decomposition.
废阴极碳(SCC)是一种来自铝电解的含有氟化物和氰化物的危险废物。许多文献都聚焦于SCC的浸出;然而,SCC的无害化处理仍未得到充分研究。本文使用10.0克原始SCC样品来探索SCC的玻璃质/高岭土固化和钙稳定化,并通过XRD和SEM方法分析其无害化机制。无论在8.0克以上玻璃质存在下于750/950℃加热60分钟,还是在8.0克以上高岭土存在下于1200℃加热120分钟,亦或是在0.5克以上碳酸钙存在下于700℃以上加热30分钟以上,浸出的氟化物均低于中国危险废物鉴别标准(GB5085.3 - 2007)。高岭土/玻璃质固化依靠大量添加玻璃质和高岭土来生成可能保留氟化物的玻璃状或类玻璃状物质(KO·AlO·6SiO)。钙稳定化将原始SCC样品中可溶的氟化钠转化为不溶的CaF。在氧气气氛中于500 - 1200℃加热60分钟几乎分解了所有氰化物,浸出的氰化物符合中国标准GB5085.3 - 2007。添加高岭土的质量损失率源于高岭石和伊利石中大量吸附水和结构水的丧失,而添加CaCO/CaSO的质量损失率归因于它们分解为挥发性的CO/SO,CaO的质量损失率略显负值是因其吸收了水蒸气和CO。简而言之,作为SCC有效的无害化方式,高岭土/玻璃质固化和钙稳定化均成功实现了氟化物的固定和氰化物的分解。