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CRT玻璃高温自蔓延反应过程中铅的挥发及纳米晶化规律研究 被引量:3

Lead Evaporation from CRT Glass and Nanocrystallization Mechanism in the High-temperature Self-propagating Process
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摘要 研究了废旧阴极射线管(CRT)玻璃高温自蔓延技术制备纳米PbO的基本过程和规律,考察了Fe2O3-Mg-CRT自蔓延体系的最高燃烧温度及燃烧波传播速率,探索了不同CRT玻璃配比对铅提取率、物相组成以及微观形貌的影响,分析了高温自蔓延反应过程中铅的挥发及纳米晶化规律,并对CRT高温自蔓延反应过程中的热力学机理和铅的挥发机制进行了初步研究.实验结果表明,随着CRT玻璃加入量的增加,高温自蔓延反应的最高燃烧温度、燃烧波传播速率和产物纳米PbO颗粒的团聚程度均呈减小的趋势.当CRT玻璃加入量为40wt%,CRT中铅的回收率约为93%,产物为球状的PbO纳米颗粒,粒径40~50 nm.本研究可以为CRT高温自蔓延处理技术的工业化应用提供一定的理论依据和数据基础. Lead evaporation and recovery of nanoparticle materials from waste cathode-ray tube(CRT) glass using the self-propagating high-temperature synthesis(SHS) method was investigated.The reaction temperature and combustion velocity of the mixture of Fe2O3-Mg-CRT in the SHS process were studied in detail.Then the lead extraction ratio,phase compositions as well as the micromorphology of extracted PbO nanoparticles were examined.The thermodynamics of lead evaporation and nanocrystallization mechanism were also analyzed.It can be found that the SHS reaction temperature and combustion velocity decrease with increasing CRT glass content,and the addition of CRT glass as a diluent can be used to control the SHS lead extraction behavior to obtain PbO nanoparticles with good desperation and morphology.With 40wt% CRT glass addition,about 93% of lead can be recovered from CRT glass as nano-sized PbO with high purity.The collected PbO nanoparticles are almost spherical in shape with particle sizes ranging from 40 nm to 50 nm,which are mainly from the volatilization and rapid condensation during the SHS process. The study indicates a novel method to recycle and reuse waste CRT glass.
出处 《无机材料学报》 SCIE EI CAS CSCD 北大核心 2012年第10期1084-1088,共5页 Journal of Inorganic Materials
基金 国家自然科学基金(20977105 50708110)~~
关键词 废旧阴极射线管玻璃 高温自蔓延技术 PBO 纳米颗粒 waste CRT glass SHS PbO nanoparticles
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  • 1罗上庚.高放废物的分离与嬗变[J].辐射防护,1996,16(1):72-75. 被引量:5
  • 2Koch L. Minor actinide transmution-a waste management option [J]. Less-Common Met., 1986, 122: 371.
  • 3Ringwood A E, Kesson S E, Ware N G, et al. Immoblisation of high level nuclear reactor wastes in SYNROC [J]. Nature, 1979,278(15): 219.
  • 4Inoue T, Sakata M, Miyashiro H, et al. Drvelopment partitioning and transmutation technology for long-lived nuclides [J]. Nucl. Technol., 1991, 93: 206.
  • 5Muthuraman M, Arul Dhas N, Patil K C. Commbustion synthesis of oxide materials for nuclear waste immobilization [J]. Bull.Mater. Sci., 1994, 17(6): 977.
  • 6Borovinskaya I P, Barinova T V, Ratnikov V I, et al. Consolidation of radioactives waste into mineral-like material by the SHS method [J]. Inter. SHS, 1998, 7(1): 129.
  • 7Barinova T V, Borovinskaya I P, Ratnikov V I, et al. SHS immobilization of radioactive wastes [J]. Kay Engineering Materials, 2002, (217): 193.
  • 8Jantzen C M, Bibler N E, Beam D C, et al. Standard test method relative to durability of nuclear waste glasses: the product consistency test (PCT) version [S]. USA, 1991. 10. 30.
  • 9张玉山.长寿命核废物嬗变处理的研究综述[J].原子核物理评论,1997,14(4):251-258. 被引量:14
  • 10罗上庚.回归自然——人造岩石固化放射性废物[J].自然杂志,1998,20(2):87-90. 被引量:33

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