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Small Tank Tetraphenylborate Process Vessel

机译:小罐四苯硼酸盐工艺容器

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One of the alternatives to processing the highly radioactive salt solutions in the Savannah River Site's Waste Tanks, is to precipitate the highly radioactive cesium with sodium tetraphenylborate concentrate, and wash the precipitate slurry. This process is called the Small Tank Tetraphenylborate Precipitation process (STTP). In the STTP process, soluble ions of cesium, potassium and ammonium are precipitated as insoluble tetraphenylborate (TPB) salts. The resulting slurry, which now contains most of the radionuclides as insoluble solids, is filtered to concentrate the solids. After washing the solids to reduce the concentration f soluble sodium salts in the slurry, the precipitate is processed and incorporated into a glass form in the Defense Waste Processing Facility (DWPF). To simplify this process, Precipitation Tank #1 is fed continuously with the volume of process water necessary to carry out the precipitation. The precipitate slurry continuously overflows to a second identical Precipitation Tank #2, which serves to increase the residence time for the precipitation process to 16-24 hours. The rate determining step is based on the absorption of the plutonium, uranium, and strontium from the solutions. The slurry exits Precipitation Tank #2 as insoluble solids and is concentrated through a crossflow filter in the Concentrate Tank. The concentrated slurry is then washed with a dilute caustic, using a crossflow filter, to reduce chemical concentrations and to achieve acceptable levels needed for glass production (Figure 1). During this process excessive foaming was observed in tests conducted using actual Savannah River Site (SRS) radioactive waste. Foaming was also observed during the precipitation, concentration, and washing steps using simulates during testing performed at the Savannah River Technology Center (SRTC). As a result of these observations, an investigation into finding suitable antifoam/defoam agents that could eliminate or mitigate foam generation was conducted by SRTC (Figures 4 and 5). The studies were conducted to develop an antifoam strategy that ensured the maximum and minimum limits needed to prevent foaming during processing of the solutions.
机译:在萨凡纳河工地的废液箱中处理高放射性盐溶液的替代方法之一是用四苯硼酸钠浓缩物沉淀高放射性铯,并洗涤沉淀浆液。此过程称为小罐四苯硼酸盐沉淀过程(STTP)。在STTP工艺中,铯,钾和铵的可溶性离子以不溶性四苯基硼酸盐(TPB)的形式沉淀。将所得的浆液过滤,以浓缩固体,该浆液现在包含大部分放射性核素作为不溶性固体。洗涤固体以降低浆液中可溶性钠盐的浓度后,将沉淀物处理并将其合并入防御废物处理设施(DWPF)中的玻璃形式。为简化此过程,连续向第1个沉淀池供入进行沉淀所需的工艺用水量。沉淀浆液连续溢流到第二个相同的沉淀池#2中,该沉淀池可将沉淀过程的停留时间增加到16-24小时。速率确定步骤基于溶液中the,铀和锶的吸收。浆液以不溶性固体形式从沉淀池#2排出,并通过浓缩池中的错流过滤器进行浓缩。然后,使用错流过滤器,用稀苛性碱洗涤浓缩的浆料,以降低化学浓度并达到玻璃生产所需的可接受水平(图1)。在此过程中,使用实际的萨凡纳河站点(SRS)放射性废物进行的测试中观察到过度发泡。在萨凡纳河技术中心(SRTC)进行的测试中,使用模拟程序在沉淀,浓缩和洗涤步骤中也观察到了起泡现象。这些观察结果的结果是,SRTC进行了寻找合适消泡剂/消泡剂的研究,以消除或减轻泡沫的产生(图4和5)。进行研究以开发消泡策略,以确保在溶液处理过程中防止起泡所需的最大和最小限制。

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