水泥固化体中Cs+浸出行为研究

Leaching Behavior of Cs+ in Cement-Solidified Waste Forms

  • 摘要: 研究了25、40、70、90 ℃下碱矿渣黏土复合胶凝材料(AASCM)和普通硅酸盐水泥(OPC)固化体中Cs+的浸出行为,并对浸出机理进行了探讨。结果表明:在25、40、70、90 ℃下,AASCM固化体和OPC固化体浸出行为不同,OPC固化体中Cs+的累积浸出分数在4个温度下趋于同一数值,而AASCM固化体中Cs+的累积浸出分数则随温度升高而增大。AASCM固化体中Cs+的存在状态为溶解态、吸附态及固溶态并存,而OPC固化体中则主要为溶解态和固溶态。AASCM固化体中处于吸附态和固溶态的Cs+接近90%,处于溶解态的约为10%;而OPC固化体中处于固溶态的约为40%,处于溶解态的约为60%。

     

    Abstract: The leaching behavior of Cs+ in alkali-activated slag-clay minerals composite cement (AASCM) and ordinary portland cement (OPC) waste forms at temperatures of 25, 40, 70, and 90 ℃ was researched. The leaching mechanism was also discussed. The results indicate that the leaching behaviors of Cs+ in the AASCM and OPC waste forms are quite different. The cumulative leaching fractions (CLF) of Cs+ in the OPC waste form tend to be a same value at the four temperatures while the CLF of Cs+ in the AASCM waste form increase with increasing temperature. In the AASCM waste form, the state of adsorption/solid solution Cs+ is about 90% and the dissolution Cs+ is about 10%. The existent state of Cs+ in the OPC waste form mainly includes the solid solution Cs+ and dissolution Cs+, which are 40% and 60%, respectively.

     

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