By Rehab O. Abdel Rahman, Ravil Z. Rakhimov, Nailia R. Rakhimova, Visit Amazon's Michael I. Ojovan Page, search results, Learn about Author Central, Michael I. Ojovan,
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IAEA (2003b) Selection of Efficient Options for Processing and Storage of Radioactive Waste in Countries with Small Amounts of Waste Generation, IAEA-TECDOC-1371. IAEA, Vienna. IAEA (2004) Treatment of Liquid Effluent from Uranium Mines and Mills, Report of a Coordinated Research Project 1996–2000, IAEA-TECDOC-1419. IAEA, Vienna. IAEA (2005a) Safety of Nuclear Fuel Cycle Facilities, IAEA Draft Document. IAEA, Vienna. IAEA (2005b) Uranium production and raw materials for the nuclear fuel cycle supply and demand, economics, the environment and energy security.
2009) Assessment of the leaching characteristics of incineration ashes in cement matrix. Chemical Engineering Journal, 155, 698–708. A. R. (2005) Disposal: a last step towards an integrated waste management system in Egypt. Proceedings of the International Conference on the Safety of Radioactive Waste Disposal, 3–7 October 2005, Tokyo, Japan. IAEA, Vienna, pp. 317–324. M. and ZakiA, A. (2007) Modeling the long term leaching behavior of 137Cs, 60Co, and152, 154Eu radionuclides from cement-clay matrices.
36 Cementitious Materials for Nuclear Waste Immobilization Tricalcium and dicalcium silicate content ranges from 75 to 80% of the mass of cement. 5) When hydration of alite and belite occurs, calcium silicate hydrates are formed with a composition and degree of crystallinity which change over wide ranges. , 1981; Taylor, 1997; Scrivener and Nonat, 2011). 6): stage 1, pre-induction with decreasing dissolution; stage 2, induction period, stage 3, acceleration period; stage 4, deceleration period; and stage 5, slowly on-going hydration.
Cementitious Materials for Nuclear Waste Immobilization by Rehab O. Abdel Rahman, Ravil Z. Rakhimov, Nailia R. Rakhimova, Visit Amazon's Michael I. Ojovan Page, search results, Learn about Author Central, Michael I. Ojovan,