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模拟含硼废液喷雾干燥试验 被引量:3

SPRAY DRYING TEST OF SIMULATED BORATED WASTE SOLUTIONS
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摘要 研究了三种喷雾干燥方式处理模拟含硼废液试验的性能和影响因素。三种喷雾干燥方式为:旋转式雾化并流喷雾干燥、气流式雾化并流喷雾干燥和气流式雾化混合流动喷雾干燥。对于硼浓度21000ppm(10-6)的模拟含硼废液,在供料温度为62~64℃,干燥塔进出口温度分别为210~220℃和110~120℃,压空流量为8.0m3/h,雾化器转速为73.0m/s的条件下,三种喷雾干燥方式均得到了流动性良好的粉体,粉体中占总质量95%的粉体粒径在0.356~0.061mm之间。三种喷雾干燥方式处理模拟含硼废液的减容系数在0.22~0.27之间,气流式雾化并流喷雾干燥方式、气流式雾化混合流动喷雾干燥方式和旋转式雾化并流喷雾干燥方式的废液处理能力依次增大,所得粉体的含水率依次增大。 Performance and the effecting factors of spray drying of simulated borated waste solutions is studied for three contaeting methods between the atomized beads and the heated air, in which boron concentration is arround 21000 ppm. The contacting modes are centrifugal atomizing co-current flow, pneumatic atomizing co-current flow and mixed flow. The results show that a free-flowing product in all these tests when the temperature of the solutions is between 62 ℃ and 64 ℃, the inlet temperature of the spray drying chamber is between 210 ℃ and 220 ℃, the temperature of the outlet of the spray drying chamber is between 110 and 120 ℃, the flow rate of the pressure air is 8.0 m^3/h, the rotational speed of the centrifugal atomizer is 73.0 m/s. The diameters of the powder product which account for 95% of the feed range from 0. 356 mm to 0. 061 mm. The production capacity and water content in the powder increase in the order of pneumatic atomizing co-current flow, mixed flow and centrifugal atomizing co-current flow. The volume reduction coeffecient of spray drying is in the ranged of 0. 22 and 0. 27.
出处 《辐射防护》 CAS CSCD 北大核心 2007年第5期297-301,320,共6页 Radiation Protection
关键词 模拟含硼废液 喷雾干燥 粉体 Simulated Borate Waste Solutions, Spray Drying,Powder
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参考文献15

  • 1IAEA.Processing of Nuclear Power Plant Waste Streams Containing Boric Acid.IAEA-TECDOC-911.Vienna,1996
  • 2Koshiba Y,Kitamura H,Kawashima A,etc.New Technologies for Treatment of Low-Level Wastes in PWR Plants.Radioactive Waste Management and Environmental Remediation-ASME.1995
  • 3佐冽藤龙明,野田哲野,铃木典子,等.含硼废弃物的处理方法和处理装置.中华人民共和国专利.CN1262513A.2000
  • 4森和秀,玉田慎,菊池恂.放射性废物固化的工艺过程和装置.中华人民共和国专利.CN85103176A.1985
  • 5Kaneko M,Toyohara M,Satoh T,et al.Development of High Volume Reduction and Cement Solidification Technique for PWR Concentrated Waste.Waste Management'01 Conference,2001.February 25~March 1
  • 6Gay R L,Grantham L F,Mckenzie D E.Volume Reduction of Reactor Wastes by Spray Drying.Proc.of the Symposium on Waste Management.Tucson,Arizona,1983.1:347
  • 7Gay R L,Grantham L F,Jones L J.Spray Drying of Bead Resins:Feasibility Tests.Proc.of the Symposium on Waste Management,1984.2:505
  • 8Gay R L,Grantham L F.Volume Reduction of Low-Level Radioactive Wastes.United States Pat.4,579,069/A/.1986
  • 9Tadamasa Hayashi,Toyoshi Mizushima.Process for Volume Reduction and Solidification of a Radioactive Sodium Borate Waste Solution.U.S.Pat.4725383.1988
  • 10阎红,王喜忠.我国干燥技术和装备的研究及应用[J].化学工程,1997,25(5):6-14. 被引量:5

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共引文献81

同被引文献25

  • 1龚立,程理,郑军华,侯运然,马小敏,姚永泉.压水堆核电站产生的硼酸废液和浓缩废液的水泥固化研究[J].辐射防护,1995,15(1):33-41. 被引量:6
  • 2车春霞,滕元成,桂强.放射性废物固化处理的研究及应用现状[J].材料导报,2006,20(2):94-97. 被引量:35
  • 3刘志辉,冯声涛,程理,王旭东,游志均.焚烧灰造粒水泥玻璃固化配方研究[J].辐射防护,2006,26(1):17-23. 被引量:8
  • 4夏尔·富歇隆,让·雅克·菲唐,埃尔韦·亚尼奥.放射性废液处理.中华人民共和国专利.CN86106420A.1986
  • 5中国建筑材料科学研究院水泥科学与新型建筑材料研究所.GB175--1999硅酸盐水泥、普通硅酸盐水泥[S].北京:中国标准出版社,1999.
  • 6中国建筑材料科学研究院.GB/T17671-1999水泥胶砂强度检验方法(ISO法)[S].北京:中国标准出版社.1999.
  • 7森和秀,玉田慎,菊池恂.放射性废物固化的工艺过程和装置[P]:中国,CN85103176A.1985.
  • 8左冽藤龙明,野田哲野,铃木典子,等.含硼废弃物的处理方法和处理装置[P]:中国,CN1262513A.2000.
  • 9陈济东,沈明道,黄世强.大亚湾核电系统及运行[M].北京:原子能出版社,1998:386-443.
  • 10时均,王家鼎,陈敏恒.粉碎、分级及团聚[M]//化学工程手册下册.第二版.北京:化学工业出版社,1996:116-134.

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