BaS与Na2S共沉淀法处理放射性废液

    Co-Precipitation Method of BaS and Na2S for Treatment of Radioactive Waste Liquid

    • 摘要: 核电厂放射性废液处理一直是个难题,主要是因为核电厂放射性废液产量大,放射性污染程度不均匀,成分复杂。目前国内核电厂对放射性废液的处理基本上都是根据废液放射性污染程度和成分不同,采用桶内蒸发干燥法、离子交换法或者移动吸附设备等进行处理。化学共沉淀法虽然研究的比较早,但一直没有得到工程应用。本研究的目的在于探索化学共沉淀法用于实际处理核电站放射性废液的可行性。根据软硬酸碱理论,选择硫化物作为放射性重金属离子的沉淀剂,理论上可以对放射性废液中的主要核素如54Mn、58Co、60Co、110Agm125Sb达到非常理想的去除效果。比较了Na2S和BaS两种硫离子供体在相同沉淀条件下对核电厂实际放射性废液的处理效果,发现BaS对实际放射性废液的处理效果更佳,一次处理就可以把样品废液中的放射性降低到达标排放水平。同时对BaS比Na2S处理效果好的原因进行了分析讨论。

       

      Abstract: The treatment of radioactive waste liquid from nuclear power plants has always been a challenge, mainly due to the large production of radioactive waste liquid, uneven levels of radioactive pollution, and complex composition. At present, the treatment of radioactive waste liquid in domestic nuclear power plants is mainly based on the degree and composition of radioactive pollution in the wastewater, using methods such as direct drying in barrels, ion exchange, or imported mobile adsorption equipment. Although the chemical co-precipitation was studied relatively earlier than most of the modern radioactive waste water treatment methods, it has not been applied in engineering. The purpose of this study is to explore the feasibility of using chemical co-precipitation method for the actual treatment of radioactive waste liquid from nuclear power plants and trying to answer the question why the chemical co-precipitation method has not been applied to practice radioactive waste water treatment. According to the theory of soft-hard acid-base theory(HSAB), sulfides are selected as precipitants for removal of radioactive heavy metal ions in this work. Theoretically, they can achieve very ideal removal effects on the main heavy metal nuclides in radioactive waste liquid, such as 54Mn, 58Co, 60Co, 110Agm, and 125Sb. This work compares the treatment effects of two sulfur ion donors, sodium sulfide and barium sulfide, on actual radioactive waste liquid from a domestic nuclear power plants, under identical precipitation condition. The carrier chemicals used for 137Cs, 60/58Co, 125Sb, 110Agm are CsCl, CoCl2•6H2O, SbCl3, AgNO3 respectively, and the concentrations of carrier nuclides for target radionuclides are 0.5 g/L each. Because most of the carrier chemicals are chlorides, to avoid any interference with the co-precipitation of the 110Agm and 137Cs, the carrier chemical AgNO3 was first added to the radioactive waste water. After AgNO3 was well dissolved, the carrier CsCl was then added followed by the addition of sodium tetraphenyl boron to precipitate 137Cs. Then the other carrier chemicals were added followed by the addition of sulfide and pH adjustment. It is found that barium sulfide has a better treatment effect on actual radioactive waste liquid than sodium sulfide. One treatment by barium sulfide can remove more than 99% radioactive nuclides except 125Sb, and reduce the radioactivity in the sample radioactive waste liquid to the standard discharge level. The removal of 125Sb is in the range of 90%-95% depending on the initial concentration of 125Sb. Barium sulfide can be used as an efficient precititant for treatment of radioactive waste water from nuclear power plant. The unsatisfactory removal of 125Sb needs further study. This work provides a preliminary discussion on the reasons why barium sulfide has a better treatment effect than sodium sulfide.

       

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