Abstract
Rare earth elements (REEs), critical to modern industry, are difficult to separate and purify, given their similar physicochemical properties originating from the lanthanide contraction. Here, we systematically study the transport of lanthanide ions (Ln3+) in artificially confined angstrom-scale two-dimensional channels using MoS2-based building blocks in an aqueous environment. The results show that the uptake and permeability of Ln3+ assume a well-defined volcano shape peaked at Sm3+. This transport behavior is rooted from the tradeoff between the barrier for dehydration and the strength of interactions of lanthanide ions in the confinement channels, reminiscent of the Sabatier principle. Molecular dynamics simulations reveal that Sm3+, with moderate hydration free energy and intermediate affinity for channel interaction, exhibit the smallest dehydration degree, consequently resulting in the highest permeability. Our work not only highlights the distinct mass transport properties under extreme confinement but also demonstrates the potential of dialing confinement dimension and chemistry for greener REEs separation.
The permeabilities of lanthanide ions in angstrom-scale 2D channels show a well-defined volcano shape.
INTRODUCTION
Rare earth elements (REEs), composed of 15 lanthanide elements (from La to Lu) and yttrium (Y) and scandium (Sc), are a unique presence in the periodic table of elements (Fig. 1A). With the progressive increase in their atomic numbers and the filling of electrons in the 4f orbitals, the lanthanides express themselves with two distinct characteristics. On the one hand, the unique electronic configuration of each lanthanide element endows individual elements with unique properties. These properties warrant the critical roles that REEs play in modern industry, ranging from high-performance alloys, catalysts, permanent magnets, lasers, etc. to the emerging quantum communications network(1, 2). On the other hand, the progressive increase in atomic number leads to the monotonic shrinking of their atomic and ionic radii, i.e., the well-known “lanthanide contraction” (3, 4). This monotonic change of atomic or ionic radii typically results in monotonic and subtle change in their physicochemical properties, e.g., Lewis acidity, hydration enthalpy, and molecular binding (1). This monotonic and subtle change of their properties, in turn, leads to the challenges of REE separations (1, 5).
Fig. 1. Competitive transport of lanthanide ions.
(A) The lanthanide ion series with referenced Al. (B) Schematic showing the transport of REE ions in the MoS2-COOH 2D channels during the competitive permeation test. The anion is nitrate and omitted for clarity. (C) Cross-sectional STEM image of MoS2-COOH membrane showing the 2D channels in the dry state. (D) XRD spectra of the MoS2-COOH membrane in the wet state in deionized water (DIW) and Ln3+/Al3+ mixture solution. PTFE is the substrate used. a.u., arbitrary units. (E) Transport results as a function of Ln3+ atomic number across the MoS2-COOH channel.
The dominant mass production of REEs includes the beneficiation of ores or other sources using concentrated acid and the subsequent separation and purification of REE both from other species and within the REE series (6). Nonetheless, the separation and purification within the REE series are fundamentally challenging, given their similarities in physicochemical properties. Current separation methods of REEs, i.e., solvent extraction, are based on the difference in partitioning of the lanthanide ions in an organic extractant phase (e.g., TBP and HDEHP) relative to an aqueous phase (usually in a strong acidic environment) (1, 7). The heavy use of organic extractants and acid leads to both heavy energy and environmental burdens (7, 8). Considerable efforts have been dedicated to exploring REE separations with both higher performances and lower negative environmental impact (6, 7, 9–13). Leading efforts have been devoted to higher-performing chelating agents, including both traditional organic extractants and recently emerging lanthanide binding peptides or proteins (14–20). Given the global increasing needs of REE for decarbonization (21, 22), it is more urgent than ever to develop greener REE production, especially the separation and purification within the REE series (7, 8).
The extractant designing strategy for REE separation is fundamentally rooted in the different chelating strengths between the lanthanide ions and the chemical extractants, including traditional organic ones or peptide-based ones. On the other hand, nature provides unmatched examples inspiring us to separate ions. Ion (e.g., K+, Na+, and Ca2+) channels in cell membranes, with angstrom-scale (Å-scale) physically confined space, have both high selectivity and fast conduction of corresponding ions across the cell membranes and thus play essential biological roles (23, 24). If we can create such highly selective artificial channels for lanthanide ion separation in a mild aqueous environment, then it would revolutionize the REE purification and substantially alleviate environmental burdens and energy consumption. Along this line, it is crucially important to understand how lanthanide ions behave under the confined space associated with Å-scale channels.
Here, we systematically study the transport and separation of lanthanide ions in model Å-scale two-dimensional (2D) channels constructed with acetic acid functionalized MoS2 nanosheets (MoS2-COOH). We chose the trivalent REE cations (Ln3+), which are the most common forms of REE cations in solution, as the model system to study. Our hypothesis underpinning the proposal is that Ln3+ cations with hydrated diameters ~9 Å should undergo a considerable dehydration process when passing through Å-scale confinement, whereby the corresponding dehydration energy penalty can be used to distinguish the REE cations, as previous works have shown for other ions (25–30). We observed that the permeability of lanthanide ions shows a volcano trend peaking at Sm3+ in such confinement in competition, deviating from the monotonic trend of single REE ion binding strength in the MoS2-COOH channel without competition. X-ray absorption spectroscopy (XAS), uptake kinetics tests, and molecular dynamics (MD) simulations reveal that Sm3+, being less dehydrated, enters the 2D channel much faster than the other REE ions which governs its dominating uptake. Moreover, with a slightly higher coordination number, Sm3+ interacts moderately with the channel which governs its fast diffusion in the 2D channel. The transport selectivity reflects a tradeoff between dehydration and binding that controls peak position in the competition of many REEs. Our work unveils the critical role of dehydration in determining the ion entrance energy (entrance sequence) and the transport energy landscape in confinement and points to the great potential for designing confinement dimension and chemistry for REE separation via transport.
RESULTS
Lanthanide transport in 2D MoS2-COOH channels
For the model system, the Å-scale confinement is built by restacking MoS2-COOH nanosheets [fig. S1, details of the functionalization method and membrane fabrication in Materials and Methods below and (31)]. The functionalization degree is ~25% per MoS2. Cross-sectional scanning transmission electron microscopy (STEM) and scanning electron microscopy images show the typical layered structure of the restacked MoS2-COOH membrane in its dry state (Fig. 1C and fig. S1).
We designed a concentration gradient (i.e., osmotic pressure)–driven permeation process to compare the permeation rates of Ln3+ across Å-scale confinement. As shown in Fig. 1B and fig. S2, a mixture containing 13 REE cations (Y3+/La3+/Ce3+/Pr3+/Nd3+/Sm3+/Eu3+/Gd3+/ Tb3+/Dy3+/Ho3+/Er3+/Yb3+) and trivalent Al3+ is used as the feed (~5 mM each cation, nitrate anion, pH ~3.6), and deionized water (DIW) (pH ~4 to 5) of the same volume is used as the permeate. A membrane constructed with MoS2-COOH 2D Å-scale channels is mounted in between. The permeation rates of each cation from the feed to the permeate are measured. All the metal cations have the same initial molarity in the feed (~5 mM) and are always exposed to the same environment, both external and internal, e.g., temperature, pressure, channel condition, and osmotic pressure. The interlayer spacing, which represents the channel height, was characterized by x-ray diffraction (XRD). The XRD spectra (Fig. 1D) indicate that the interlayer spacing of the MoS2-COOH membrane in the wet state (pure DIW) is ~11.1 Å, and it increases to ~12.5 Å in the Ln3+/Al3+mixture solution during transport. Considering the intrinsic thickness of a monolayer MoS2 sheet (~6.2 Å), the effective channel height for transport of the mixed ions in the MoS2-COOH membrane is ~6.3 Å (versus ~4.9 Å in the pure DIW), implying a bilayer-water structure in the 2D channel. Moreover, XRD measurements show that the MoS2-COOH membrane is stable in the mixture solution for a relatively long term (fig. S3).
Inductively coupled plasma mass spectrometry (ICP-MS) was used to identify and quantify individual cations in both the feed and the permeate. The concentration changes of all cations over time were simultaneously monitored (fig. S4). Water level difference was also observed, indicating water flow from the permeate to the feed (fig. S5). These observations indicate the tendency toward equilibrium across the MoS2-COOH membrane, as confirmed by the decrease of osmotic pressure across the membrane (fig. S6). However, the ions show three different concentration profiles in the test window: equilibrium, nonequilibrium, and crossover between the feed and the permeate (fig. S4). The qualitative difference suggests that the ions have different transport speeds across the MoS2-COOH 2D channels.
Quantitative analyses are further made based on the permeation rates, Pi (mol/s) (see calculation details in Material and Methods). Al3+ is used as the reference. The relative ion permeation rates of lanthanide ions versus Al3+, PLn3+/PAl3+, across the MoS2-COOH channels range from ~1.6 to ~2.3. This fact indicates that Ln3+ can permeate through the 2D channel much faster than Al3+. This can be attributed to the fact that Al3+ has the largest hydration enthalpy in the group: the hydration enthalpy of Al3+ is −4715 kJ/mol, much larger than that of Yb3+, −3740 kJ/mol (32). Since the hydration enthalpy characterizes the interactions between ions and water molecules within their hydration shells, larger ionic hydration enthalpy also indicates larger ionic hydration radius in bulk solution and larger energy barrier for ions to overcome when passing through the confinement. PLn3+/PAl3+ values show a clear volcano shape peaking at Sm3+ (Fig. 1E and fig. S7). This observation is uncommon for the lanthanides, given that lanthanides typically show monotonic property changes due to the lanthanide contraction mentioned above. We note that this volcano-shaped transport behavior is robust in all tests using different MoS2-COOH membranes (fig. S7B). Similar volcano shape is also observed when Na+ is used as the reference, although PLn3+ are ~3- to 5-fold smaller than PNa+ (fig. S8). Likewise, this can be attributed to the much smaller hydration enthalpy of Na+ (−405 kJ/mol). In addition, changing the lanthanide ion combination (using Y3+/La3+/Ce3+/Nd3+/Eu3+/Tb3+/Dy3+/Yb3+) results in a similar volcano shape in transport (fig. S9). As a comparison, a commercial porous polytetrafluoroethylene (PTFE) membrane (nominal pore size, ~200 nm) was used for the transport test. Experimental measurement shows that PLn3+/PAl3+ decreases monotonically with increase in atomic number when passing through the PTFE membrane (fig. S10). The monotonic decrease for the PTFE membrane is consistent with the change of bulk diffusion coefficients (33, 34) and can be explained by the monotonic increase in hydration enthalpy. Notably, although the adjacent pair selectivity in the MoS2-COOH 2D channels is lower than those in organic extractants, ranging from ~1.01 to ~1.07, it is higher than those in the PTFE membrane (or the bulk) with typical values below 1.01 (fig. S11). This comparison suggests that confinement can be a tool used to enhance the separation selectivity of REE ions. To explain the uncommon volcano shape in the transport trend observed for lanthanide ions in the 2D channels, we examined the thermodynamics and kinetics of REE cations in the MoS2-COOH channels.
Thermodynamics
First, the ion uptake in the mixture solution was measured. The results indicate that the uptake amounts of REE cations in the MoS2-COOH membrane also show a clear volcano shape, peaking at Sm3+ (figs. S12 and S13). Independent uptake tests using the MoS2-COOH membrane show that the binary separation values between La3+/Ce3+, La3+/Yb3+, Sm3+/La3+, and Sm3+/ Yb3+ are ~1.4, ~1.4, ~2.5, and ~1.7, respectively (fig. S14). Given that the coordination modes between Ln3+ and lanthanide binding proteins (e.g., lanmodulin) play an important role (17, 19, 20), we probed the ion coordination in 2D MoS2-COOH using infrared (IR) spectroscopy. On the basis of the ion-carboxylate coordination peak position, Ln3+ adopt a combination of monodentate and bidentate binding modes with the carboxylate groups, while Al3+ only adopts the monodentate binding mode (Fig. 2, A and B) (35). The single ion uptake results show that the uptake amounts follow an increasing trend with heavier REE ions having larger uptake, which indicates stronger interactions between heavier REE and the MoS2-COOH (fig. S15). The stronger interactions between the heavier REE ions with the MoS2-COOH walls can be further corroborated by the XRD measurements of single salt treated MoS2-COOH membranes. With increase in the atomic number of Ln3+, the right shift of both (002) and (004) peaks suggests a decrease in the interlayer spacing in the MoS2-COOH channel (Fig. 2, C to E). Note that the hydration radius in the bulk solution is expected to increase with atomic number, given the increase in their Lewis acidity (36). In other words, the decreasing trend of the interlayer spacing in the single Ln3+ treated MoS2-COOH channel is exactly against their ionic hydration radius trend, which thus should be attributed to stronger interactions between heavier REE ion and the MoS2-COOH walls.
Fig. 2. Structures of lanthanide ions in the 2D channels.
(A) The effect of different metal cations on the IR absorption spectra of the carboxylate group in the MoS2-COOH membranes. The dashed lines are the corresponding negative second-order derivatives of the absorption spectra (solid lines) for peak pinpointing. (B) Schematic illustrations of the protonated/deuterated carboxylate group (i), free carboxylate group (ii), the monodentate (iii), and bidentate (iv) coordination mode between metal cations and carboxylate group. (C and D) The (002) and (004) peaks of the XRD spectra of the MoS2-COOH membrane with individual Ln3+/Al3+ ions, respectively. Note that (004) peak is absent in the air-dry sample, DIW-soaked sample and the Al3+-soaked sample. Except for the air-dry sample without any ions, other samples were measured in their wet state. (E) The interlayer spacing change of the MoS2-COOH channel with individual Ln3+ ions in the wet state. (F) EXAFS spectra of La3+ in the bulk solution and in the MoS2-COOH membrane.
Then, we turned to synchrotron XAS to probe the coordination environment of REE ions in the 2D confinement (Fig. 2F and fig. S16, details in Materials and Methods below). The fitting results are listed in table S1. The result shows that in bulk solution, light REE ions (La3+/ Sm3+) have ~9 water molecules, and the heavy REE ion (Dy3+) has ~8 water molecules in their first hydration shell, consistent with both previous experimental results (37) and MD simulations (34). By comparison, in 2D confinement, the coordination number of Sm3+ decreased by ~3.0, and La3+ and Dy3+ decreased by 3.3. This result has two implications. First, a significant amount of dehydration in the first hydration shell occurred for REE ions adsorbed in the 2D MoS2-COOH channels, indicating a critical role of the dehydration barrier for transport in confinement; second, the dehydration degree is different among REE ions with Sm3+ having less dehydration. The larger degree of dehydration for La3+ could be due to its larger bare ion size such that it requires a smaller coordination number to fit into the channel. The larger degree of dehydration for Dy3+ could be resulting from the stronger interaction with the MoS2-COOH channel. On the basis of the results, we propose an intuitive picture, purely from the perspective of thermodynamics, to explain the volcano shape of the uptake result observed in the 2D confined channels. With the increase in the atomic number, the increase of Lewis acidity (or the shrinking of ionic radii) of REE ions plays a dual role: On one hand, heavier REE ions would have stronger interactions with the MoS2-COOH walls, which thus translate into their thermodynamic advantages in confinement; on the other hand, heavier REE ions would have a higher dehydration energy penalty to overcome when going from the bulk solution into the 2D channels. Therefore, the tradeoff between the dehydration barrier and strength of interactions for the Ln3+ ions in 2D confinement leads to the volcano shape observed, a mechanism reminiscent of the Sabatier principle well-established in catalysis (38) and reported recently for designing ultrastable nanocatalysts (39).
We noticed that for the MoS2-COOH membrane uptake results, the single ion uptake pattern (increasing trend) is notably different from that for the REE mixture (volcano trend). This difference can be explained from the changes in thermodynamics and the membrane uptake kinetics. Take Yb3+ as an example. In the single-solute solution, Yb3+ exhibits the smallest interlayer spacing (~12.0 Å) in its thermodynamically stable state among REE ions. By comparison, in the mixture uptake experiment, the interlayer spacing is ~12.5 Å (Ln3+/Al3+ mixture; Fig. 1D) or 12.9 Å (Ln3+ mixture without Al3+; see “pH effect”), larger than the thermodynamically stable interlayer spacing for the single Yb3+. Thermodynamically, the larger interlayer spacing leads to a reduction in the binding affinity between Yb3+ ions and MoS2-COOH, which is consistent with the decrease in uptake found in the mixed ion experiment. In addition, as will be comprehensively discussed in the next section (“MD simulations and kinetics”), the kinetics of ion entrance to the channels and ion interaction in the channels also play significant roles, and this is important to both uptake and transport.
MD simulations and kinetics
To further advance our understanding of ion transport within 2D MoS2-COOH channels, we conducted all-atom MD simulations (Fig. 3A). The interlayer spacing (Mo-Mo distance) was set to be 12.5 Å, consistent with the experiment (more details in the Supplementary Materials). We simulated ion transport from the feed into the channel by applying high pressure to the piston wall (Fig. 3A). The fluxes of REE cations into the channel and into the permeate are depicted in Fig. 3B. Notably, the flux of cations into the permeate effectively reproduces the experimentally observed volcano shape of the REE cations across the MoS2-COOH channel (Fig. 1D). The greater initial flux of cations into the channel compared to that into the permeate can be attributed to the high-energy barrier arising from the attractive electrostatic interactions between REE cations and ─COOH/─COO− groups inside the MoS2-COOH channel. In addition, these findings indicate that Sm3+ exhibits the fastest uptake from the feed into the channel. The dynamics of membrane uptake using the REE mixture solution was tested in our measurements, and indeed the uptake of Sm3+ shows the fastest uptake rate into the membrane (Fig. 3C), which is consistent with the MD simulations. Please note that the simulated mixture used in this study represents a simplified model in comparison to the experimental setup (details in the Supplementary Materials). Nonetheless, the trends extracted from our simulations align coherently with the experimental observations and provide atomistic-level insight into the underlying mechanisms governing ion transport.
Fig. 3. MD simulations and kinetics.
(A) Simulation modeling of REE cations transport through 2D MoS2-COOH channels, which includes six extra MoS2 sheets as the supporting membrane (Mo in yellow and S in gray), water (transparent blue), ions (in black, blue, red, green and cyan) and two MoS2 sheets as piston wall (in gray). (B) MD simulations results showing the fluxes of REE cations into the MoS2-COOH channel, the fluxes of REE cation into the permeate, and the hydration free energy (HFE). Here, the flux in this study is determined by linearly fitting the time evolution of ion entry into the channel or into the permeate. Our analysis is confined to the times where the ion counts increase most rapidly. (C) Experimental data showing the dynamics of Ln3+ uptake in the MoS2-COOH membrane. Note that Sm3+ is plotted in both figures for better comparison. (D) Averaged diffusion coefficients of Ln3+ cations and Cl− anions in the MD simulations. (E) A schematic diagram of the energy barrier landscape for REE cations transport in the MoS2-COOH channel. The color of the curves is chosen to match that of the bars for the same element in (D).
Subsequently, we performed calculations to determine the diffusion coefficients of REE cations and Cl− anion (see Fig. 3D and fig. S19). The diffusion coefficients of REE cations entering and passing through the channel both showed a volcano-shaped pattern, with Sm3+ exhibiting the highest diffusion coefficient. The diffusion coefficient of Cl− is 1.5 to 4 times higher than that of REE cations, suggesting that Cl− does not significantly participate in the diffusion of REE cations. To further confirm this, we evaluated the ratio of REE cations that pass through the membrane and the ratio of REE cations that are knocked (i.e., interact at a distance that is 3.5 Å or less) by Cl− and pass through the membrane, respectively (fig. S20). Our analysis revealed a lack of correlation between these two ratios, indicative of the independent transport of REE cations and Cl− anions as they permeate the MoS2-COOH channel. This indicates that ion-pair formation is not significant to the transport.
Factors such as ion pairing, dehydration, and the interaction between ions and membranes are recognized as primary determinants governing the ion transport mechanism (40). Given that ion pairing is not important to the observed volcano shape, our subsequent focus shifts to elucidating the dehydration effect and ion-membrane interactions. We first computed the hydration free energy (HFE) of REE cations in the bulk solution (see Fig. 3B), which reveals a positive correlation with the atomic number, aligning with the tabulated hydration enthalpy values in Fig. 1E. Furthermore, we performed a series of umbrella sampling simulations to obtain the potential of mean force (PMF) for REE cations permeating the membrane (fig. S21). According to the PMF results, we categorized the difficulty of ion permeation into three levels: “easy penetrating,” including La3+ and Pr3+ cations (level I); “medium penetrating,” represented by Sm3+ (level II); and “difficult penetrating,” including Gd3+ and Dy3+ (level III). It is important to note that the PMF displays variability when distinct pathways are selected, as depicted in fig. S22, and our PMF simulations focus on the transport of individual ions rather than a mixture of ions. Therefore, the PMF data provided serve exclusively as a reference for evaluating the binding affinity between REE cations and ─COOH/─COO− groups and should not be construed as an accurate representation of actual permeation phenomena for REE mixtures.
The results above indicate that Sm3+ exhibits a moderate degree of HFE and binding affinity with ─COOH/─COO− groups, consistent with the experimental measurements (Fig. 2, C to F). To gain insight into its impact on the dehydration effect during permeation, we investigated changes in the coordination number within the first solvation shell of the REE cations (fig. S23). On the one hand, the La3+ and Pr3+ cations can more easily lose or gain water (1 to 2 water) during the process of passing through the channel, attributable to their weaker HFE and binding affinity with ─COOH/─COO− group. On the other hand, because of their robust binding affinity with the ─COOH/─COO− group, Gd3+ and Dy3+ cations experienced a loss of 0.8 to 1.1 water molecules during the permeation process. Together with their higher HFE, these ions encountered the highest-energy barrier while traversing the channel. Unexpectedly, the Sm3+ cation, which has an intermediate HFE and binding affinity with the ─COOH/─COO− group, exhibited the lowest degree of dehydration (0.2 to 0.5 water) when passing through the channel, which is in qualitative agreement with XAS data (table S1) and thus results in the highest permeation rate. Note that the dehydration number we extract here is the dehydration number for transport, which is different from the dehydration number for uptake that was extracted from the XAS data. In addition, we examined the dwell time of REE cations in the vicinity (3.5 Å) of ─COOH/─COO− groups, which reveals a positive correlation with atomic number, with the exception of the Sm3+ cation (fig. S24). This observation is consistent with the fact that the Sm3+ cation experiences the least dehydration during permeation.
On the basis of the above discussion and previous studies (40–42), we propose a diagram to qualitatively illustrate the energy barrier landscape for REE cation transport in MoS2-COOH channels (Fig. 3E). In the entry phase, REE cations undergo a dehydration penalty and electrostatic attraction reward with the MoS2-COOH channel. These factors collectively contribute to a kinetically determined dehydration barrier at the entrance to the channel and then a well once the ions coordinate to acetate near the entrance. If we denote the difference between the barrier and well energies as EEntry, then the effective diffusion coefficient of cations entering the channel is determined by (EEntry~RTlnDEntry) (3). As depicted in (Fig. 3 B to D), the Sm3+ cation exhibits the fastest uptake (largest DEntry) from the solution into the membrane for mixed ion transport, implying that this cation should have the largest value of EEntry. Likewise, the energy barrier governing intramembrane diffusion (EDiffusion) can be inferred from the diffusion coefficient within the membrane (EDiffusion~ –RTlnDDiffusion) (fig. S19), suggesting that Sm3+ cation has the lowest EDiffusion (Fig. 3E for mixed transport). Consequently, Sm3+ holds the lowest-energy barrier for ion transport through the membrane (ETransport), thereby manifesting the highest permeability. Further, MD simulations show that a slight increase (5%) in the channel height leads to REE transport behavior deviating from the volcano shape, indicating its sensitivity to the confinement dimension (fig. S25).
pH effect
Further data analysis reveals a prominent fact in the uptake: The ratios of Ln3+ to ─COOH (∑NM3+/N-COOH) in all the membrane uptake tests using mixed REE solution with concentration ranging from 0.1 to 10 mM (corresponding pH range from ~3.6 to ~4.7; fig. S12) are only around 30%. This fact further leads us to a question: What is the role of the protonation/deprotonation of ─COOH in the uptake and transport? To approach this question, we conducted membrane uptake experiments at different pH values, ranging from ~4.7 to ~7.1 (concentration: 0.1 mM, details in Materials and Methods below). The result is shown in Fig. 4A. At pH ~4.7, the membrane uptake of Ln3+ basically shows a volcano shape peaking at Sm3+, consistent with the aforementioned results. However, upon increase in pH, the uptake amount of Ln3+ increases due to enhanced deprotonation. Further analyses show that the ratio of ∑NM3+/N-COOH is likely to increase to over 100% at pH ~7.1 (table. S2), which points to the possibility of Ln3+ coordinating with sulfur atoms in the MoS2-COOH 2D channels. Meanwhile, the shape of the Ln3+ uptake curve gradually changes into a monotonically increasing function as pH increases. This presumably reflects a change in the tradeoff between dehydration penalty and electrostatic attraction when the ─COOH gets deprotonated as pH is increased. It is also noteworthy that there seems to be a discontinuity in the curves in Fig. 4A at Gd3+ (atomic number 64). This might suggest the empirical “Gadolinium break” argument for REEs (43), which remains to be clarified.
Fig. 4. pH effect on uptake and transport.
The uptake (A), interlayer spacing (B), and permeation rate (C) of Ln3+ in the MoS2-COOH channels at different pH values.
XRD measurements show that the interlayer spacing of the MoS2-COOH 2D channels increases from 12.9 Å at pH ~4.7 to 13.5 Å at at pH ~7.1 (Fig. 4B). This suggests that the enlarged channel spacing will decrease the dehydration penalty for Ln3+ entering into the 2D confinement. Therefore, at high pH, the enhanced binding due to enhanced deprotonation and the decreased dehydration barrier due to enlarged interlayer spacing break the tradeoff between dehydration and strength of interactions with confinement channels, which in turn contributes to the enhanced uptake of heavier Ln3+ (Fig. 4A). However, in the transport experiments (details in Materials and Methods below), the permeability of Ln3+ at both pH ~7.1 and pH ~4.7 shows a similar volcano shape (Fig. 4C and fig. S26), which is unexpected given that the uptake trend is different at different pHs. A possible scenario we propose here is that a significant fraction of Ln3+ ions that are absorbed into the 2D channels, particularly the heavier ones, is trapped. Thus, their thermodynamic advantage (larger uptake) does not straightforwardly translate into a higher permeabilty in the 2D channel. More efforts are needed to clarify the difference between uptake and transport at high pH nonetheless.
Given that the tradeoff of Ln3+ cannot be fine-tuned by pH in the MoS2-COOH channels, we tried to explore Ln3+ transport in the 2D confinement by changing the confinement environment as a final effort. In the pristine MoS2 channels without any functionalization or with amide-functionalized MoS2 (MoS2-CONH2) channels (31), what we observed is basically a monotonically decreasing trend, instead of a volcano shape, for PLn3+ as a function of atomic number (figs. S27 and S28), suggesting a lack of the tradeoff noted above. All combined, we conclude that the tradeoff enabling the volcano shape observed is sensitive to both the confinement dimension and confinement chemistry.
DISCUSSION
To sum up, we systematically studied the transport of lanthanide ions in model Å-scale 2D MoS2-COOH channels in an aqueous environment. A volcano-shaped transport trend of lanthanide ions is observed. Both the thermodynamics and kinetics of ion transport under 2D confinement are systematically analyzed. The results indicate that controlling the dehydration degree and binding strength of lanthanide ions in the 2D channel are critical in governing a smooth energy landscape for transport. Our current experimental and MD simulations results point to the possibility of tuning REE selectivity with different functional groups in the 2D channels. It also implies the possibility of achieving REE separations in 1D or 0D confinement with delicate functionalization. All these efforts would facilitate the inverse design of selective REE separation materials.
MATERIALS AND METHODS
Preparation of mixed ions solution
Al(NO3)3·9H2O/La(NO3)3·6H2O/Ce(NO3)3·6H2O/Pr(NO3)3·6H2O/Nd(NO3)3·6H2O/Sm(NO3)3·6H2O/Eu(NO3)3·6H2O/Gd(NO3)3·6H2O/Tb(NO3)3·6H2O/Dy(NO3)3·5H2O/Ho(NO3)3·5H2O/Er(NO3)3·5H2O/Yb(NO3)3·5H2O were used as salts. Al(NO3)3·9H2O (98 + %) was purchased from Strem Chemicals. All REE salts were purchased from Neta Scientific Inc. with 99 + %purity. All chemicals were used without further treatment.
The concentration of aqueous Al3+/Ln3+ mixture solution was ~5 mM for each cation with intrinsic pH ~3.6. Note that all the salt solutions used in the tests, either the single salt solution or the mixture solutions of varied combinations, have intrinsic pH values (typically acid) after salt dissolve without further tuning, unless stated below.
To explore the pH effect for REE separation, we chose a low concentration of Ln3+ mixture solution (~0.1 mM with intrinsic pH ~4.7) to enlarge the tunability of the pH window. KOH aqueous solution (0.5 M) was used to tune the pH of Ln3+ mixture solution. No precipitation was observed when pH of the Ln3+ mixture solution was tuned up to ~7.2. Further, increasing the pH leads to the precipitation of Ln3+. For the same reason, Al3+ was kicked out of the Ln3+ mixture, because it precipitated out upon the addition of KOH.
Preparation of MoS2-COOH dispersion solution
First, the single- or few-layer MoS2 nanosheet aqueous dispersion solution was prepared through the intercalation of MoS2 powders (Sigma-Aldrich) in n-butyl lithium/hexane solution (1.6 M) (Caution!), as widely reported previously. Then, the acetic acid functionalization of the MoS2 nanosheet was achieved through its nucleophilic reaction with iodoacetic acid (ICH2COOH, purchased from Sigma-Aldrich), as we reported in (31) of the main text. Our previous measurement shows that the functionalization degree is ~25% ─COOH per MoS2.
Preparation of MoS2-COOH membrane
Before membrane preparation, to remove possible ion contaminations, the prepared MoS2-COOH dispersion solution is washed with dilute trace-metal HCl (~2 to 5 mM), which is followed by filtration and redispersion in water under sonication (~10 to 15 min). The “HCl washing-filtration-redispersion” cycle was repeated at least three times. Then, the redispersed MoS2-COOH solutions is dialyzed in dialysis tubings (Sigma-Aldrich, part no. D9527-100FT) to remove extra HCl. Last, repeated centrifugation (~4000 rpm/10 min) is used to get the aqueous dispersion solutions of single- or few-layer MoS2-COOH nanosheets (concentration, 0.1 to 0.2 mg/ml), which were stored in HCl-washed plastic bottles and under 4°C for use.
The MoS2-COOH membrane is prepared via the vacuum-assisted filtration method. The substrate used is PTFE (fig. S10,; pore size: 0.2 μm; purchased from Sigma-Aldrich, part no. JGWP04700). Upon filtration, the MoS2-COOH/PTFE complex membrane is transferred to clean petri dishes for overnight air drying. Note that to avoid membrane shrinkage or deformation, before membrane transfer, several drops of DIW is put beneath the complex membrane to remove air bubbles between PTFE and dishes. Then, the air-dried complex membrane is used for ion transport tests, membrane uptake tests, and other characterizations like XRD and XAS tests. Our previous study (31) shows that the as-prepared MoS2-COOH composite membrane has good mechanical strength, which can withstand high pressure at least >10 bar.
The competitive permeation test of mixed ions across the membranes
Experimental protocol
A pair of H-cells was used for the competitive permeation test of mixed ions across the membranes, including the porous PTFE membrane and MoS2-COOH/PTFE complex membrane. These membranes are mounted in between the H-cells by commercial Silicon paste. The H-cells are ready for permeation tests upon solidification of the Silicon paste.
In a competitive permeation test of mixed ions, 21 ml of solution of mixed ions (either 5 mM Al3+/Ln3+ mixture or Ln3+ mixture) and 21 ml of DIW were simultaneously poured into the feed side and the permeate side of H-cells, respectively. For the transport test using 0.1 mM Ln3+ with pH 7.1 (fig. S26), the pH of the DIW in the permeate side was tuned to be ~7.1 at the very beginning of the test. Note that the MoS2-COOH faces the feed side for the MoS2-COOH/PTFE complex membrane. Both chambers are strongly stirred to avoid concentration polarization throughout the permeation tests. Then, the concentration changes of every metal cation were monitored through periodic samplings (10 to 100 μl per sampling subject to change according to permeation time), which were then diluted by 3% HNO3 to 3 to 5 ml for ICP-MS measurements. Both chambers were tightly sealed with parafilm to avoid undesired evaporation throughout the process, except when sampling.
Quantitative analyses
To perform quantitative analysis, we focus on the ion concentration changes in the permeate side in the early stage, which show a linear increase versus time (figs. S7A, S8, A to C, S9A, S10D, S26, S27A, and S28A). By calculating the slopes of linear profiles, we can get the permeation rates of all the ions, Pi (mol/s). The permeation rate of Al3+ or Y3+ or Na+ is used as a reference. Pi values are plotted. We note here that although a level difference between the feed chamber and the permeate chamber can be always observed in the long-time test, this difference was very small in the early stage for a few hours and volume changes of both chambers were typically <2%.
The IR tests
The prepared MoS2-COOH membranes were transferred from the PTFE substrate to 1-mm-thick CaF2 substrates for IR absorption measurements. Before IR measurements, the membranes were soaked in individual salt solution (1 M in D2O, purchased from Fisher Scientific, part no. M1133660100) overnight to achieve ion uptake equilibrium and were gently dried with tissue to remove the excess water immediately before the measurement. All spectra were measured in a Bruker Hyperion microscope coupled to a Bruker Vertex 70 FTIR spectrometer. The measurements were performed with a 0.4–numerical aperture (NA) Schwarzschild objective resulting in an IR focal spot of 100-μm diameter. Measurements were repeated to ensure the region of the sample was spatially uniform. Spectra were measured with a 2-cm−1 resolution, and 32 scans were averaged. The second derivative spectra were determined using a differentiating Savitztky-Golay filter.
Membrane uptake test
MoS2-COOH membranes were soaked into relevant solutions for at least overnight to achieve uptake equilibria. Note that for the membrane uptake kinetics test in Fig. 3B, the uptake time lasted for given durations as shown. After membrane uptake test, the membrane was taken out and thoroughly washed with flowing DIW (for ~2 min) to remove the mixed ions solution remaining on the surface. Then, the washed membranes were dissolved in 3 ml of HNO3 (3%) under sonication overnight. Last, the leaching HNO3 solution was filtered and diluted for ICP-MS measurement.
XAS measurement
MoS2-COOH membrane was soaked in the mixture solution of La3+/Pr3+/Sm3+/ Gd3+/Dy3+/Yb3+(~5 mM, natural pH after salts dissolving without tuning). This mixture combination is to increase the loading of each single REE cation to increase the signal-to-noise ratio in XAS measurements while maintaining the volcano-shaped uptake observed (as confirmed in fig. S13B).
XAS experiments were carried out at 5BM-DND, Advanced Photon Source of Argonne National Laboratory. All the K-edge XAS measurements of La3+, Sm3+, and Dy3+ were conducted under fluorescence mode by a Vortex ME4 detector. All XAS data analyses were performed with Athena software package to extract x-ray absorption near-edge structure and extended x-ray absorption fine structure (EXAFS). Fourier transform of La3+, Sm3+, and Dy3+ was performed by using Hanning window function with k-weights of 2 and k-range from 3 to 10 Å−1. For model-based EXAFS analysis, all the scattering paths were generated by the FEFF calculation function in Artemis based on the crystal structure of La(H2O)9, Sm(H2O)9, and Dy(H2O)8. The generated scattering paths were then calibrated by performing the FEFF of the EXAFS data of those reference solution samples, mainly to obtain the amplitude reduction factor (S02) values. With S02 known, all EXAFS data of the membranes were fitted.
All-atom MD simulations
We performed all-atom MD simulations to study the cooperative transport of mixed REE (La3+/Pr3+/Sm3+/Gd3+/Dy3+) cations in the MoS2-COOH membranes. Our model (Fig. 3A) consists of a bilayer MoS2 sheet acting as a rigid piston wall to exert external pressure, an ion-filled feed region, a multilayered MoS2 membrane serving as an ion channel, and a pure water permeate region. The multilayered MoS2 membrane can be visualized as extracting two layers of MoS2 from bulk crystals (2H-MoS2) and being modified with corresponding acetate functional groups while leaving a 12.5-Å interlayer spacing (Mo-Mo distance) that is consistent with the experiment. Other MD simulations details are provided in the Supplementary Materials.
Acknowledgments
Funding: This work is supported by the Department of Energy, Office of Basic Energy Science, under grant DE-SC0022231. This work made use of instruments in the Electron Microscopy Core of UIC’s Research Resources Center. This research used resources of the Advanced Photon Source, a US Department of Energy (DOE) Office of Science user facility operated for the DOE Office of Science by Argonne National Laboratory under contract no. DE-AC02-06CH11357.
Author contributions: Mingzhan Wang and C.L. conceived the idea. Mingzhan Wang designed the experiments, performed the tests, and analyzed the data. Q.X. conducted MD simulations under the supervision of G.C.S. N.H.C.L. conducted the IR measurements and analyses. Maoyu Wang and H.Z. performed XAS measurements and analyses. G.Y. and D.Y. contributed to ICPMS tests. Y.H. performed cross-sectional TEM imaging. E.H. and G.P. contributed to material preparation and transport data analyses. O.-S. L. contributed to the MD simulations. Mingzhan Wang, Q.X., G.C.S., and C.L. wrote the manuscript with inputs from all the authors. G.C.S. and C.L. supervised the project.
Competing interests: The authors declare that they have no competing interests.
Data and materials availability: All data needed to evaluate the conclusions in the paper are present in the paper and/or the Supplementary Materials.
Supplementary Materials
This PDF file includes:
Figs. S1 to S28
Table S1 to S3
Notes S1 to S3
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Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Supplementary Materials
Figs. S1 to S28
Table S1 to S3
Notes S1 to S3




