Benoît D. L.
Campéon
ab,
Tetsuya
Ishikawa
a,
Kuriyama
Tomohiro
a and
Naoaki
Yabuuchi
*a
aAdvanced Chemical Energy Research Center, Institute of Advanced Sciences, Department of Chemistry and Life Science, Yokohama National University, 79-5 Tokiwadai, Hodogaya-ku, Yokohama, Kanagawa 240-8501, Japan. E-mail: yabuuchi-naoaki-pw@ynu.ac.jp
bUniversity Grenoble Alpes, University Savoie Mont Blanc, CNRS, Grenoble INP, LEPMI, Grenoble, France
First published on 4th December 2024
The air stability and moisture sensitivity of titanium-based layered negative electrode materials for sodium storage play a critical role in their practical applications for advanced energy storage systems. However, the impact of moisture exposure on the electrochemical performance of these materials, as well as the potential for recovery through post-calcination treatment, remains unexplored. In this study, the impact of reactions with water molecules through exposure to moisture with high relative humidity and water soaking treatment on crystal structures and electrochemical performance in Na cells of titanium-based layered oxides is explored. The exposure to water molecules results in proton insertion associated with ion-exchange of sodium ions and the formation of sodium hydroxide, which further absorbs carbon dioxide. The removal of protons by post-calcination treatment requires relatively higher temperature, but the metastable layered oxides with oxygen vacancies, which show superior sodium storage reversibility, are newly obtained. The possibility of improvement of air stability and its practical reality for sodium battery applications are also discussed through a mechanistic study on moisture exposure of titanium-based electrode materials.
Previous studies have explored the impact of moisture exposure and soaking on sodium-containing layered oxides with different transition metal ions, especially for positive electrode materials.23 For instance, Manthiram et al. reported the moisture-induced degradation of an O3-NaNi0.7Mn0.15Co0.15O2 positive electrode, resulting in decreased electrochemical performance due to reactions with H2O and CO2.24 In addition, the reaction with moisture results in Na+/H+ ion-exchange, and the presence of H+ in the Na+ layers leads to the complicated structural evolution of layered sodium-positive electrode materials upon exposure to air and moisture.25,26 In addition, a recent study by Zuo et al. aims to advance the understanding of the interconnections between these complex reactions, particularly the factors influencing the insertion of water molecules into the Na+ layers and the determinants of the extent of structural transformation.27 They found that the redox potential for transition metal ions plays a critical role in the air stability of P2-NaxTmO2, with higher redox potential leading to improved stability. These studies emphasized the critical importance of moisture stability and highlighted the need for effective strategies to mitigate the detrimental effects of moisture exposure on these materials.
Presently, previous research has provided important insights into the effects of moisture on layered sodium positive electrode materials. However, the knowledge of air stability of layered titanium-based negative electrode materials is limited. Generally, to increase theoretical capacities, titanium layered oxides with Na ions are designed with high sodium deficiency, which would influence moisture reactivity. Therefore, further studies are needed to expand our understanding and find strategies to expedite the practical implementation of layered titanium negative electrode materials for Na battery applications.
In this study, we aim to build upon previous research by systematically studying the effect of exposure to moisture and soaking in water on layered sodium negative electrode materials, specifically focusing on four Ti-based layered phases with different compositions and layered stackings. By comparing the Ti-based layered materials with different layered stacking modes, P2 and P3 phases, as well as examining the impact of layered phases substituted by different metal components, Cr3+, Mg2+, and Li+ ions, we seek to gain a comprehensive understanding of the structural and electrochemical changes induced by the presence of moisture. Furthermore, we will explore the potential of calcination as a post-treatment method to recover and enhance the performance of materials exposed to moisture/soaked in water. The outcomes of this study will contribute to the development of moisture-tolerant layered Ti-based layered negative electrode materials and provide valuable insights for the design and optimization of practical sodium-ion battery systems. By elucidating the effects of moisture on these materials and proposing strategies for performance recovery, we aim to advance the field of energy storage and enable the practical implementation of cost-effective sodium-ion batteries in various applications.
To assess the robustness of the prepared materials, moisture exposure and water soaking tests were conducted, as depicted in Fig. 2a. The moisture exposure resistance test involved incubating the powder samples in a chamber at 100% relative humidity (RH) and 20 °C for 5 days. The samples obtained from these tests were labeled as RH P2 NaCrTiO, RH P3 NaCrTiO, RH P2 NaCrMgTiO, and RH P2 NaLiTiO. The monitoring of mass changes before and after the moisture exposure test indicates gravimetric increases of 27, 30, 59, and 71% for P2 NaCrMgTiO, P2 NaLiTiO, P2 NaCrTiO, and P3 NaCrTiO, respectively, foreseeing less water absorption for P2 NaCrMgTiO and P2 NaLiTiO. Structural evaluations of these samples by X-ray diffraction (XRD), reported in Fig. 2b and ESI Fig. S1,† reveal structural changes in RH P3 NaCrTiO and RH P2 NaCrTiO. Specifically, their 003 and 002 diffraction lines are shifted to lower angles, indicating increases in interlayer distances from ∼5.6 to ∼7.0 Å. This increase suggests that during the moisture exposure resistance test, water molecules are intercalated between metal oxide layers as illustrated in Fig. 2c. Interestingly, RH P2 NaLiTiO shows no shift to lower angles, but new peaks are visible (Fig. 2b and ESI Fig. S1†), indicating that although P2 NaLiTiO is affected by moisture, it maintains its structural integrity in the presence of Li ions. Because these new peaks are found in the regions with higher diffraction angles for the original P2 layered phase (ESI Fig. S1†), this new phase has the same P2 layered structure with shorter lattice parameters, probably originating from partial Na+/H+ ion-exchange upon moisture exposure. This process also results in the accumulation of NaOH on the particle surface, and NaOH further reacts with CO2, leading to the appearance of new peaks for the crystalline phase. This phase is further analyzed in the later section. In addition to the ion-exchange process, as reported by Victor Duffort et al.,31 CO2 insertion into the crystal lattice of P2 NaLiTiO is also another possibility, which potentially influences the lattice parameter change after the moisture exposure test. Notably, the Mg-substituted sample, P2 NaCrMgTiO, shows no significant structural changes, without the formation of a new phase, during the moisture exposure resistance test, indicating its superior robustness against moisture. Nevertheless, water absorption at the oxide surface and partial ion-exchange cannot be eliminated as discussed in the later section.
Observation of the samples' morphology by scanning electron microscopy (SEM), as reported in ESI Fig. S2 and S3,† indicates no critical changes caused by the moisture exposure test, except for RH P2 NaLiTiO. Additional smaller particles with a needle-like morphology appear, which is consistent with XRD observation. Remarkably, under a high-energy electron beam, these needle-like particles were decomposed, underscoring the need for mild conditions during its characterization. Elemental mapping by energy-dispersive X-ray spectroscopy (EDX) of RH P2 NaLiTiO given in ESI Fig. S4† shows that the Na distribution is richer for these new particles, further supporting the Na+/H+ exchange and formation of NaOH on the P2 NaLiTiO surface upon moisture exposure.
Additionally, a water soaking test, as illustrated in Fig. 2a, was conducted by directly immersing the powder samples in distilled water for 3 hours, followed by filtration and vacuum drying at 60 °C. During the soaking test, the pH of solutions increased within 30 minutes above pH = 10, which corroborates the presence of basic compounds with Na ions in solutions. The obtained samples preserved their original color and were labeled SK P2 NaCrTiO, SK P3 NaCrTiO, SK P2 NaCrMgTiO, and SK P2 NaLiTiO. In good agreement with the moisture exposure resistance test, the water soaking test confirms the structural instability of P2 NaCrTiO and P3 NaCrTiO, as their interlayer distances reach ∼7.0 Å, contrasting with the structural stability of P2 NaCrMgTiO and P2 NaLiTiO. As expected, SK P2 NaLiTiO does not present a peak adjacent to its 002 diffraction line, which corroborates the formation of a crystalline alkaline compound, visualized in ESI Fig. S4,† but it is a water-soluble species and is dissolved in water from the P2 NaLiTiO surface during the water soaking test.32 The SEM analysis of these samples, reported in Fig. 2d–g and ESI Fig. S2 and S3,† shows clear cracks for all water-soaked samples. It should be noted that only for SK P2 NaCrTiO, these cracks are easily found and visualized due to its interlayer expansion and relatively large particle size, ∼1 μm. In agreement with the XRD observation of SK P2 NaLiTiO, the SEM observation indicates that the side product is effectively washed away from its surface during the water soaking test. Indeed, as illustrated in Fig. 2a, water filtered from all samples was dried to obtain white powders, which were labeled EX P2 NaCrTiO, EX P3 NaCrTiO, EX P2 NaCrMgTiO, and EX P2 NaLiTiO. Structural examination via XRD analysis of EX P2 NaCrTiO, shown in ESI Fig. S5,† indicates that these materials correspond to Na2CO3. Attenuated total reflectance Fourier-transform infrared (ATR-FTIR) spectroscopy analysis of these powders (Fig. 2h) reveals that the spectra of all samples show peaks mainly corresponding to Na2CO3 (ESI Fig. S6†).33 In agreement with the above results, it indicates that all samples, including structurally stable P2 NaCrMgTiO and P2 NaLiTiO, undergo Na+/H+ exchange upon soaking in water. Assuming that these white powders are mainly composed of Na2CO3, the gravimetric analysis indicates that structurally unstable P2 NaCrTiO and P3 NaCrTiO exchange approximately 60 and 33% of their Na+ ions, while structurally stable P2 NaCrMgTiO and P2 NaLiTiO exchange only 23% and 20% of their Na+ ions, respectively. Additionally, the filtered water before evaporation was analyzed by ultraviolet-visible (UV-vis) absorption spectroscopy, as shown in ESI Fig. S7† and Fig. 2i. These values were calibrated from the correlation between the aqueous solution absorbance and concentration of NaOH and Na2CO3 from UV-vis spectra (ESI Fig. S8†). The analysis of these solutions' concentration observes 69, 45, 23, and 22% Na+ extracted for P2 NaCrTiO, P3 NaCrTiO, P2 NaCrMgTiO, and P2 NaLiTiO, respectively. These findings align with the ATR-FTIR and UV-vis spectra illustrated in Fig. 2a, indicating that upon exposure to water molecules, Na+/H+ exchange proceeds for all samples, but its extent and insertion of water molecules depend on the layered stacking modes and chemical compositions. The extracted Na+ forms NaOH, resulting in the formation of Na2CO3 after CO2 absorption in air. In the moisture exposure test, the Na2CO3 remains on the sample surface, while during soaking in water, Na+ ions are dissolved in water from the sample surface. Among the tested samples, P2 NaCrMgTiO and P2 NaLiTiO show better air stability with less Na+/H+ ion-exchange without H2O intercalation into the crystal lattice, even though shoulder peaks, which are indicative of partial H2O insertion, are observed for SK P2 NaCrMgTiO.
To explore recovery routes of water exposed samples by thermal treatment, preliminary thermogravimetry (TG) analysis was conducted. TG curves of the samples after exposure to moisture or soaking in water with their differential curves are shown in Fig. 3a. The results indicate that all water-soaked samples show two mass loss regions, from 50 to 100 °C and from 100 to 600 °C, while all moisture-exposed samples present an additional mass loss region from 500 to 835 °C. All these regions seem to be composed of several peaks, which denotes that the mass loss involves several consecutive mass loss mechanisms during heating. To determine the mechanism involved in each mass loss region, mass spectroscopy analysis was conducted for RH P2 NaLiTiO and RH P2 NaCrMgTiO. The mass spectra (Fig. 3b) indicate that as expected, the first mass loss region, from 50 to 100 °C, corresponds to the removal of H2O adsorbed on the surface of the material. For RH P2 NaCrTiO and RH P3 NaCrTiO, a more dramatic mass loss is observed, indicating that more moisture is absorbed by those samples. The second region, from 100 to 600 °C, displays formation of different gases for RH P2 NaLiTiO and RH P2 NaCrMgTiO. Indeed, RH P2 NaCrMgTiO mostly releases H2O in this region, corresponding to the removal of H+ from its Na layers, which was further confirmed by mass spectroscopy (Fig. 3b). Additionally, RH P2 NaLiTiO releases CO2 in this region, attesting to the presence and removal of CO32− from the transition metal layer of this sodium metal oxide. The third region, from 500 to 835 °C, is characterized by the release of CO2. This region is only found for moisture-exposed samples, indicating that CO2 release in this region originates from the decomposition of Na2CO3 present on the sample surface. To clarify the role played by CO2, additional moisture-exposed samples have been prepared in the absence of CO2. Remarkably, similar to the results previously published for layered sodium positive electrode materials,34 the mass gain is decreased for all our layered sodium negative electrode materials, Table S1.† However, structural study via XRD analysis, presented in Fig. S9,† indicates no clear difference between samples prepared with and without CO2. TG results obtained for samples exposed to moisture in the absence of CO2, presented in Fig. 3a, display no third region, confirming that the peak in that region for moisture-exposed samples correspond to the decomposition of Na2CO3 present on the sample surface resulting from the reaction between NaOH and CO2. It is also noted that in the absence of CO2, all samples exhibit an additional decomposition peak between 500 °C and 600 °C, which could originate from the decomposition of NaOH and/or the reaction of oxides with Na2O formed by NaOH decomposition in the absence of CO2. Additionally, RH P2 NaCrTiO and RH P3 NaCrTiO exhibit even stronger Na+/H+ exchange because H2O removal, associated with the elimination of H+ from the lattice, is expected to proceed in the higher temperature region, ∼600 °C, which is further discussed in the later section. H2O release at higher temperatures is intensified for both samples.
To further track the structural evolution during the re-calcination process, an XRD study was conducted for the heat-treated samples, as shown in Fig. 3c, S10, and S11.† As foreseen, all the moisture-exposed and water-soaked samples after re-calcination above 600 °C recover close to their original structures and similar interlayer distances without impurities. However, peak widths are broadened compared with the as-prepared samples. Na+/H+ ion-exchange samples, for instance, Na2/3−yHyCr1/3Mg1/2Ti1/2O2, are formed, and H+ removal from Cr1/3Mg1/2Ti1/2O2 is expected to be achieved with oxygen extraction from the crystal lattice, leading to the formation of a metastable phase with oxygen vacancies, i.e., Na2/3−yCr1/3Mg1/2Ti1/2O2−y/2 + y/2H2O.·CO2 insertion into the lattice and the loss of CO32− ions on heating would influence phase transition processes. Indeed, for the P2 NaLiTiO system, the re-calcination is also accompanied by the presence of an additional peak at 45.0°. The formation of a new phase is also clearly visualized as changes in the particle morphology in Fig. S2 and S3.† An attempt to identify any differences in chemical compositions by EDX mapping is unsuccessful, and no visible atomic distribution difference is observed, as shown in Fig. S4.† When the re-calcination temperature is further increased above 835 °C for moisture-exposed samples, the same diffraction patterns with the as-prepared samples are observed, indicating that metastable phases formed by the loss of H+/CO32− on heating react with Na+ ions formed by Na2CO3 decomposition. In contrast, a different trend is noted for water-soaked samples, and a new phase is formed after heating at 1000 °C. These peaks can be assigned to a hollandite phase, which is a typical sodium-deficient phase, for instance Na2/5Cr2/5Ti3/5O2.35
These studies identify two distinct thermal recovery pathways, as depicted in Fig. 4, one for moisture-exposed samples and another for water-soaked samples. As observed previously, both moisture exposure and soaking in water lead to Na+/H+ exchange in Ti-based layered materials, resulting in the formation of partially desodiated and protonated samples, such as Na2/3−xHxCr1/3Mg1/6Ti1/2O2 coupled with NaOH formation. However, moisture exposure results in the accumulation of Na2CO3 on the surface, whereas soaking in water leads to the dissolution of NaOH in the solution. The extracted Na+ ions are further separated from the sample via filtration. For moisture-exposed samples, upon calcination, intercalated H+ is released as H2O couples with oxygen vacancy formation in the framework structure, forming metastable phases. The phases obtained by H+ extraction further reacts with Na2CO3, regenerating the as-prepared phase, P2 Na2/3Cr1/3Mg1/6Ti1/2O2, as illustrated in Fig. 4. For water-soaked samples, extracted Na+ is lost by filtration; therefore, upon calcination, metastable phases obtained by H+ extraction decompose on further heating to 1000 °C, leading to the formation of a P2-type layered oxide and a non-layered sodium-deficient phase with Ti ions.
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Fig. 4 A schematic illustration of proposed structural changes upon calcination after the water soaking or moisture exposure test. |
Finally, to assess the robustness of the Ti-based layered electrode materials against moisture exposure and soaking in water, electrochemical characterization was performed using a half-cell configuration with metallic sodium as the counter electrode in 1.0 mol dm−3 NaPF6 dissolved in propylene carbonate used as the electrolyte and an electrode composed of active materials, acetylene black, and the poly(acrylonitrile)-grafted poly(vinyl alcohol) copolymer (PVA-g-PAN).36 Note that poly(vinylidene fluoride) (PVdF), which is often used as a binder for battery applications, easily shows gelation when an alkaline residue is present in the sample, and therefore it is difficult to use PVdF as a binder for the moisture-exposed samples.37–39 Galvanostatic charge/discharge curves in the first cycle, as presented in Fig. 5a, show that both moisture-exposed and water-soaked samples exhibit lower discharge (oxidation) capacities compared to the pristine samples stored in the Ar-filled glove box. This capacity loss is also accompanied by a decrease in the initial coulombic efficiency (ICE). Interestingly, the moisture exposure test appears more detrimental to the electrode materials compared to the water soaking test. This outcome could be attributed to the fact that the surface of the samples is damaged by the formation of NaOH and the accumulation of Na2CO3 during moisture exposure, which forms the high resistance layer for Na+ exchange between oxides and electrolyte solutions. Among the samples, P2 Na2/3Cr1/3Mg1/6Ti1/2O2 shows nearly unchanged capacity retention after both moisture exposure and water soaking tests (Fig. 5b). Subsequently, P2 NaCrTiO, P3 NaCrTiO, P2 NaCrMgTiO, and P2 NaLiTiO were recalcined at 650, 835, 650, and 850 °C, respectively. For the water-soaked samples, recalcination restores the ICE; however, the reversible capacity is reduced because of the surface damage. The formation of a hollandite phase is also noted for P2 NaLiTiO, which reduces the reversible capacity as electrode materials. Nevertheless, recalcined P2 Na2/3Cr1/3Mg1/6Ti1/2O2 after soaking in water exhibits a higher reversible capacity, >100 mA h g−1, compared with the as-prepared sample, indicating that the sodium-deficient metastable phase, P2 Na2/3−xCr1/3Mg1/6Ti1/2O2−x/2, shows superior reversibility without surface degradation. The increase in the vacant sites after H+ removal from the layered oxides results in a larger reversible capacity as electrode materials. For the moisture-exposed samples, recalcination partially restores the original reversible capacity for P2 NaCrTiO and completely restores it for P3 NaCrTiO and P2 NaCrMgTiO, as shown in Fig. 5, where recalcination recovers the initial crystal structure for these samples. However, for P2 NaLiTiO, recalcination of the moisture-exposed and water-soaked samples leads to capacity decay, which is consistent with the fact that a new phase is formed after recalcination (Fig. 3c). Upon cycling, as presented in Fig. 5b, S12, and S13,† the recovery of moisture-exposed samples shows promising results for all chromium/titanium-based systems, especially for the Mg-substituted sample, with the original capacity and CE maintained during the first 50 cycles. In contrast, P2 NaLiTiO exhibits only 90% of its original capacity associated with the phase segregation as mentioned above. Although the degradation by moisture exposure is a practical problem for Ti-based layered materials, P2 NaCrMgTiO shows better stability and recovery for electrode performance after re-calcination, which is a superior characteristic for battery applications.
Footnote |
† Electronic supplementary information (ESI) available. See DOI: https://doi.org/10.1039/d4ta07033j |
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