journal article·2024-05Open access

Effect of glass forming additives on low-activity waste feed conversion to glass

Miroslava Vernerová, Karolína Šůsová, Martina Kohoutková, Jaroslav Kloužek, Petra Cincibusová, Pavel Ferkl, Jose Marcial, Pavel Hrma, Albert A. Kruger, Richard Pokorný

Abstract

A significant effort was invested in the past to develop and refine mathematical models that relate the composition of nuclear waste glasses with their properties, such as viscosity, electrical conductivity, or chemical durability. However, less attention has been paid to the formulation of the melter feed itself, such as the chemical form and the particle size of the glass forming and modifying additives, which have a significant effect on the feed-to-glass conversion process during melting. To address this issue, we systematically changed the mineral composition of a simulated low-activity waste melter feed and inspected its melting behavior. When substituting minerals with corresponding oxides and hydroxides, we found that different alumina sources (kyanite, gibbsite, boehmite, or corundum) had the strongest effect on the feed melting process, whereas the sources of Ca, Mg, and Zr had little effect. The X-ray diffraction analysis showed that the alumina sources differ in their dissolution kinetics: early dissolving alumina sources, such as gibbsite (Al(OH) 3 ) and boehmite (AlO(OH)), increase the transient glass-forming melt viscosity at early stages, when gases still evolve, causing extended foaming, whereas alumina sources that dissolve at high temperatures, such as kyanite (Al 2SiO 5 ) and corundum (Al 2O 3), keep the transient glass-forming melt viscosity low and lead to a faster foam collapse. Using a viscosity-composition relationship to estimate the viscosity of transient glass-forming melts in the primary foaming range, we found that the primary foam began to collapse at 360 to 800 Pa s, and fully collapsed between 65 and 260 Pa s. This result agrees with our previous studies, according to which, the glass-forming melt viscosity at the cold cap foam bottom ranged from 24 to 85 Pa s.
Source: expertdata · Quality: candidate unverified · Source record ↗

Research context

OpenAlex topics: Glass properties and applications · Recycling and utilization of industrial and municipal waste in materials production · Pigment Synthesis and Properties

SciVX discovery tags are terminology-based. OpenAlex topics are source-provided classifications.

References (64)

Show source-provided references
1. Turning nuclear waste into glass10.1063/PT.3.2687 ↗
2. Advances in JHCM HLW Vitrification technology at VSL through scaled melter testing
3. Nuclear waste vitrification in the united states: recent developments and future options10.1111/j.2041-1294.2010.00023.x ↗
4. A history of Hanford tank waste, implications for waste treatment, and disposal10.1002/ep.13567 ↗
5. Challenges with vitrification of Hanford High-Level Waste (HLW) to borosilicate glass – an overview
6. Hanford low-activity waste vitrification: a review10.1016/j.jhazmat.2023.132437 ↗
7. Impacts of constraints and uncertainties on projected amount of Hanford low-activity waste glasses10.1016/j.nucengdes.2021.111543 ↗
8. A data-driven approach for predicting nepheline crystallization in high-level waste glasses10.1111/jace.17122 ↗
9. Parsimonious viscosity–composition relationships for high-temperature multicomponent glass melts10.1080/21870764.2021.2012903 ↗
10. Vienna · 2022
11. Glass property models, constraints, and formulation approaches for vitrification of high-level nuclear wastes at the US Hanford site10.4191/kcers.2015.52.2.92 ↗
12. Hanford low-activity waste glass composition-temperature-melt viscosity relationships10.1111/ijag.16580 ↗
13. Towards increased waste loading in high level waste glasses: developing a better understanding of crystallization behavior10.1016/j.mspro.2014.10.012 ↗
14. Glass formulation development in support of melter testing to demonstrate enhanced high level waste throughput
15. Compositional models of glass/melt properties and their use for glass formulation10.1016/j.mspro.2014.10.020 ↗
16. Machine learning with gradient-based optimization of nuclear waste vitrification with uncertainties and constraints10.3390/pr10112365 ↗
17. Effect of Al and Fe sources on conversion of high-level nuclear waste feed to glass10.1016/j.jnucmat.2021.153423 ↗
18. Model for the conversion of nuclear waste melter feed to glass10.1016/j.jnucmat.2013.11.009 ↗
19. Mathematical modeling of cold cap: effect of bubbling on melting rate
20. Effects of heating rate, quartz particle size, viscosity, and form of glass additives on high-level waste melter feed volume expansion10.1111/jace.14629 ↗
21. Effects of alumina sources (gibbsite, boehmite, and corundum) on melting behavior of high-level radioactive waste melter feed10.1557/adv.2016.644 ↗
22. Corrosion of Ni-Cr alloys in molten salts and hanford law waste Glass
23. Corrosion of Inconel 690 and Inconel 693 in an iron phosphate glass melt10.1016/j.corsci.2013.05.027 ↗
24. Numerical comparison of bubbling in a waste glass melter10.1016/j.anucene.2017.11.044 ↗
25. Glass production rate in electric furnaces for radioactive waste vitrification10.1111/jace.16463 ↗
26. Conversion kinetics of container glass batch melting10.1111/jace.17406 ↗
27. Model for batch-to-glass conversion: coupling the heat transfer with conversion kinetics10.1080/21870764.2021.1907914 ↗
28. Conversion kinetics during melting of simulated nuclear waste glass feeds measured by dissolution of silica10.1016/j.jnoncrysol.2021.121363 ↗
29. Effect of cold cap coverage and emissivity on the plenum temperature in a pilot-scale waste vitrification melter10.1111/ijag.15031 ↗
30. Heat transfer from glass melt to cold cap: computational fluid dynamics study of cavities beneath cold cap10.1111/ijag.15863 ↗
31. Heat transfer from glass melt to cold cap: gas evolution and foaming10.1111/jace.16484 ↗
32. Cold-cap reactions in vitrification of nuclear waste glass: experiments and modeling10.1016/j.tca.2013.02.016 ↗
33. Viscosity of glass-forming melt at the bottom of high-level waste melter-feed cold caps: effects of temperature and incorporation of solid components10.1111/jace.16876 ↗
34. Melting rate correlation with batch properties and melter operating conditions during conversion of nuclear waste melter feeds to glasses10.1111/ijag.15911 ↗
35. Effect of material properties on batch-to-glass conversion kinetics10.1111/ijag.16631 ↗
36. Conversion degree and heat transfer in the cold cap and their effect on glass production rate in an electric melter10.1111/ijag.16615 ↗
37. Through a glass darkly: in-situ x-ray computed tomography imaging of feed melting in continuously fed laboratory-scale glass melter10.1016/j.ceramint.2021.02.153 ↗
38. Matlack · 2018
39. Cluster formation of silica particles in glass batches during melting10.1016/j.jnoncrysol.2010.04.009 ↗
40. A method for determining bulk density, material density, and porosity of Melter feed during nuclear waste vitrification10.1111/jace.13919 ↗
41. Rietveld refinement guidelines10.1107/S0021889898009856 ↗
42. Quantitative analysis of crystalline and amorphous phases in glass–ceramic composites like LTCC by the Rietveld method10.1111/j.1551-2916.2006.01113.x ↗
43. Conversion of nuclear waste to molten glass: cold-cap reactions in crucible tests10.1111/jace.14310 ↗
44. Conversion of nuclear waste to molten glass: formation of porous amorphous alumina in a high-Al melter feed10.1016/j.jnucmat.2016.11.005 ↗
45. Structural Characterization of Ternary Salt Melts for Low Activity Waste Applications10.1557/adv.2019.136 ↗
46. Transient melt formation and its effect on conversion phenomena during nuclear waste vitrification - HT-ESEM analysis
47. Effect of sucrose on foaming and melting behavior of a low-activity waste melter feed10.1111/jace.16675 ↗
48. Heat transfer from glass melt to cold cap: effect of heating rate10.1111/ijag.13104 ↗
49. Refining in the Glassmelting Process10.1111/j.1151-2916.1977.tb15528.x ↗
50. The semiempirical model of the multicomponent bubble behavior in glass melts
51. Beerkens · 2002
52. Gas release and foam formation during melting and fining of glass10.1111/j.1551-2916.2005.00691.x ↗
53. Dissolution retardation of solid silica during glass-batch melting10.1016/j.jnoncrysol.2011.03.041 ↗
54. Temperature distribution within a cold cap during nuclear waste vitrification10.1021/acs.est.5b00931 ↗
55. In situ characterization of foam morphology during melting of simulated waste glass using x-ray computed tomography10.1016/j.ceramint.2020.02.215 ↗
56. In-situ X-ray and visual observation of foam morphology and behavior at the batch-melt interface during melting of simulated waste glass10.1016/j.ceramint.2021.11.344 ↗
57. Augmented Adam-Gibbs model for glass melt viscosity and configuration entropy as functions of temperature and composition10.1016/j.jnoncrysol.2022.121832 ↗
58. Glass length: workability and meltability of glass as a function of glass melt fragility10.1016/j.jnoncrysol.2022.121931 ↗
59. Effect of alumina source on the rate of melting demonstrated with nuclear waste glass batch10.1111/j.2041-1294.2012.00079.x ↗
60. Effect of aluminum-containing raw materials on the melting of borosilicate glass for fiber10.1016/j.ceramint.2021.07.283 ↗
61. Design of new energy-friendly compositions
62. Jordan-Hernandez · 2005 · 84
63. Results of the successful introduction of Calumite into a green container furnace
64. Influence of the increased content of Calumite blast-furnace slag on the melting of sodium–calcium–silicate glass10.1007/s10973-019-08895-1 ↗