Preliminary Investigations on the Pyrometallurgical Recycling of a TiMn2–Based Hydrogen Storage Alloy
Abstract
1. Introduction
- Simulation of deactivated end-of-life Hydralloy C5 by synthesizing with varying levels of oxygen and nitrogen contamination;
- Characterization of synthetically deactivated end-of-life as well as virgin Hydralloy C5 (ICP-OES, XRD, hot gas extraction, microscopic and SEM-EDX analysis);
- Determination of Hydralloy C5’s basic properties in the molten state (melting/solidification temperature and vapor pressure) experimentally and by simulation;
- Preliminary remelting trials of the synthetically deactivated end-of-life materials via VIM and CCAM (including investigation of the interaction between liquid Hydralloy C5 and selected refractory materials).
1.1. Hydralloy C5—A Short Overview
1.2. Criticality of Raw Materials and Supply Risks
1.3. Ecological Impact of Hydralloy C5
2. Preparatory Work
2.1. Synthesis of Deactivated End-of-Life Hydralloy C5
2.1.1. Composition and Gas Analysis
2.1.2. X-Ray Diffraction
2.1.3. Microscopic and SEM-EDX Analysis
2.2. Determination of Basic Alloy Properties
3. Materials and Methods
3.1. Cold Crucible Arc Melting (CCAM)
3.2. Vacuum Induction Melting (VIM)
3.2.1. Selection of Suitable Refractories
3.2.2. VIM Procedure and Material
4. Results and Discussion of Remelting Trials
4.1. Cold Crucible Arc Melting (CCAM)
4.1.1. Material 1 (Low Contamination)
4.1.2. Material 2 (High Contamination)
4.2. Vacuum Induction Melting (VIM)
4.2.1. Material 1 (Low Contamination)
4.2.2. Material 2 (High Contamination)
5. Summary
6. Conclusions and Outlook
- Once the method for gently opening the real storage containers has been established, we will know the exact level of O and N contamination that needs to be adjusted for during recycling. This real contaminated end-of-life Hydralloy C5 can then be compared with the simulated materials from this publication. This applies not only with regard to chemical composition, morphology or particle size distribution, but particularly with regard to melting behavior.
- We will remelt the real end-of-life Hydralloy C5 with the realistic contamination level in the VIM and CCAM, if necessary with the gradual addition of the deoxidizer cerium mixed metal, which is also used in primary alloy production. With regard to the separation of non-metallic inclusions and thus to avoid crucible wall deposits, we will conduct several VIM trials using fluxes. The remelting tests to be carried out in the CCAM and VIM in the future will be accompanied by H2 capacity measurements.
- Further refractory–melt interaction tests will take place in the VIM, this time using only virgin 2–10 mm Hydralloy C5. Refractory materials such as magnesium aluminate spinel and refractories coated with Y2O3 and fired will be used.
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Acknowledgments
Conflicts of Interest
Abbreviations
| VIM | Vacuum Induction Melting |
| PIM | Pressure Induction Melting |
| CCAM | Cold Crucible Arc Melting |
| PESR | Pressure Electro Slag Remelting |
| ESR | Electro Slag Remelting |
| HSA | Hydrogen Storage Alloy |
| ICP-OES | Inductively Coupled Plasma Optical Emission Spectroscopy |
| SEM-EDX | Scanning Electron Microscopy with Energy Dispersive X-ray spectroscopy |
| NiMHB | Nickel Metal Hydride Battery |
| XRD | X-ray Diffraction |
| LCA | Life Cycle Assessment |
| CED | Cumulative Energy Demand |
| GWP | Global Warming Potential |
| DSC | Differential Scanning Calorimetry |
| CRM | Critical Raw Materials |
| SRM | Strategic Raw Materials |
| BCC | Body-Centered Cubic |
| BSE | Backscattered Electrons |
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| Input Materials for Hydralloy C5 | EU Criticality (2023) [22] | EU Import Reliance (Primary) [22,23] | EU Import Reliance (Refined) [22,23] |
|---|---|---|---|
| Iron deriv. from [3,17] | Iron (not CRM) Coke (CRM) | 77% (Ore) 66% (Coking coal) | 5% (Pig iron, DRI, granules and powders, crude steel) 0% (Coke, tar, benzole, ammonia, coke oven gas) |
| Aluminum [17] | Aluminum/Bauxite (CRM, SRM) | 89% (Bauxite) | 58% (Refined alumina, unwrought aluminum) |
| Vanadium oxide [17] | Vanadium (CRM) | 100% (Ore, concentrate, crude oil, slag from steelmaking) | 100% (Vanadium oxide, FeV, other chemical compounds) |
| Electrolytic manganese [1,2,8] | Manganese (CRM, SRM) | 96% (Ore) | 61% (FeMn, FeSiMn, manganese) |
| Titanium (Ti-Sponge) [21] | Titanium (CRM, SRM) | 100% (Ore, concentrate) | 18% (Ti-Sponge) 100% (Titanium) |
| Zirconium [23] (Zr-Sponge) [2,7] | Zirconium (no CRM) | 83% (Zircon sand) | 27% (Zirconium) |
| Cerium mischmetal [21] | Cerium (CRM, SRM) Lanthanum (CRM) | 100% (Cerium concentrates) 100% (Lanthanum concentrates) | |
| Alloy | Form | Crucible | Temp. [°C] | Hold. Time [min] | Main Take Away | Ref. |
|---|---|---|---|---|---|---|
| TiFe0.86Mn0.10 | elemental | CaO-ZrO2 (98-2 wt.%) Graphite | 1500–1600 | 5–10 | O content same for both, while C heavily increased in graphite case which went along with sticky TiC attachments | [29] |
| Ti0.85Zr0.15Mn1.22Ni0.22Cr0.2V0.3Fe0.06 | elemental | Graphite Y2O3-lined Al2O3-SiO2 | 1600–1800 | 1 | Despite the 0.05-inch spray-painted Y2O3 layer, the melt in both crucibles was partially contaminated | [28] |
| Ti1-xZrxCry1Mny2Niy3 Fey4Vy5 | elemental | Al2O3-based | 1600–1800 | 1–5 | Contamination of ingots (oxides, sub-oxides and Ti-rich precipitates) from melt–crucible interaction but still acceptable H2 capa. | [2] |
| (In wt.-%) | Al2O3 | CaO | ZrO2 | SiO2 | Fe2O3 | TiO2 | Porosity [%] | Volume [mL] |
|---|---|---|---|---|---|---|---|---|
| CaO-stabilized ZrO2 | - | 4 | 94 | 0.4 | - | - | 20.5 | 600 |
| Titanium aluminate | >70 | - | - | - | - | <30 | 18 | 600 |
| (In wt.%) | Ex. 1 | Ex. 2 | Ex. 3 | Ex. 4 | Ex. 5 |
|---|---|---|---|---|---|
| Process steps | Two | Two | Two | Two | One |
| CerMM input | 2.0 | 1.0 | 0.6 | 2.0 | 3.0 |
| O in MnFeV | 0.040 | 0.023 | 0.040 | 0.023 | - |
| O in Hydralloy C5 | 0.040 | 0.050 | 0.040 | 0.030 | 0.260 |
| CerMM in Hydralloy C5 | 0.55 | 0.16 | 0.13 | 0.85 | 0.51 |
| H2 capacity | 2.04 | 1.96 | 2.01 | 2.05 | 1.85 |
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Krusenbaum, J.; Selvan, A.; Friedrich, B. Preliminary Investigations on the Pyrometallurgical Recycling of a TiMn2–Based Hydrogen Storage Alloy. Materials 2026, 19, 1804. https://doi.org/10.3390/ma19091804
Krusenbaum J, Selvan A, Friedrich B. Preliminary Investigations on the Pyrometallurgical Recycling of a TiMn2–Based Hydrogen Storage Alloy. Materials. 2026; 19(9):1804. https://doi.org/10.3390/ma19091804
Chicago/Turabian StyleKrusenbaum, Jan, Ajithkumar Selvan, and Bernd Friedrich. 2026. "Preliminary Investigations on the Pyrometallurgical Recycling of a TiMn2–Based Hydrogen Storage Alloy" Materials 19, no. 9: 1804. https://doi.org/10.3390/ma19091804
APA StyleKrusenbaum, J., Selvan, A., & Friedrich, B. (2026). Preliminary Investigations on the Pyrometallurgical Recycling of a TiMn2–Based Hydrogen Storage Alloy. Materials, 19(9), 1804. https://doi.org/10.3390/ma19091804

