Plasma Gasification of a Simulated Low-Level Radioactive Waste: Co, Cs, Sr, and Ce Retention Efficiency
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Published:2024-09-06
Issue:9
Volume:12
Page:1919
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ISSN:2227-9717
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Container-title:Processes
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language:en
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Short-container-title:Processes
Author:
Pullao Juan Ariel123, Benedetto Franco Emmanuel12, Binetti Basterrechea Gian Franco4, Neira Poblete Leonardo Andrés1, Lago Diana Carolina15ORCID, Prado Miguel Oscar6
Affiliation:
1. Departamento Materiales Nucleares, Comisión Nacional de Energía Atómica, Av. Exequiel Bustillo 9500, San Carlos de Bariloche 8400, Río Negro, Argentina 2. Facultad de Ciencias Exactas y Naturales (FCEN), Universidad Nacional de Cuyo (UNCuyo), Padre Jorge Contreras, M5502 JMA, Mendoza 1300, Argentina 3. Escuela de Producción, Tecnología y Medio Ambiente, Universidad Nacional de Río Negro (UNRN), Anasagasti 1463, San Carlos de Bariloche 8400, Río Negro, Argentina 4. Facultad Regional de Buenos Aires (FRBS), Universidad Tecnológica Nacional (UTN), Mozart 2300, Ciudad Autónoma de Buenos Aires C1407, Argentina 5. FunGlass—Centre for Functional and Surface Functionalized Glass, Alexander Dubček University of Trenčín, 911 50 Trenčín, Slovakia 6. Consejo Nacional de Investigaciones Científicas y Técnicas (CONICET), Av. de los Pioneros 2350, San Carlos de Bariloche 8400, Río Negro, Argentina
Abstract
Thermal plasma is a versatile technology that can be used to treat various types of wastes, including vegetal and mineral oils, solvents, plastics, paper and cardboard, glasses, bricks and rocks, metals, clothes, and mixtures of these materials. In this study, we utilized a commercial plasma cutter as a thermal plasma source to decrease the volume of a simulated low-level radioactive mixed solid waste. The simulated waste included papers, plastics, clothes, gloves, metals, and stable Co, Cs, Sr, and Ce additives as surrogates of 60Co, 137Cs, 90Sr, and 144Ce, respectively, the latter being typical contaminants in nuclear LLW. As a result of the process, two products were obtained: a solid phase, on which we focused this work, and a gaseous phase. To retain as many as surrogates as possible in the solid final phase, crushed glass from broken bottles was included as a vitrification additive to the original waste. After undergoing heat treatment, a dense vitreous slag was produced along with ashes. The process resulted in a volume reduction of 70%, indicating the successful gasification of organic excess materials. The surrogate elements were retained in the process and were found in the ashes composition: Co (3.4% w/w), Cs (37.7% w/w), and Ce (0.6% w/w) and in the glass matrix composition of Co, Cs, Sr and Ce: 72.4 ± 14.7, 32 ± 18.2, 125.3 ± 31.6, 80 ± 13.1% w/w, respectively. For the actual experimental conditions, retention efficiencies were estimated for cobalt (Co) at 72.4 ± 14.7%, cerium (Ce) at 80 ± 13.1%, strontium (Sr) at 125.3 ± 31.6%, and notably cesium (Cs) at 32 ± 18.2%.
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