Anion-adaptive crystalline cationic material for 99TcO4 trapping


Efficient anion recognition is of great significance for radioactive 99TcO4 decontamination, but it remains a challenge for traditional sorbents. Herein, we put forward a tactic using soft crystalline cationic material with anion-adaptive dynamics for 99TcO4 sequestration. A cucurbit[8]uril-based supramolecular metal-organic material is produced through a multi-component assembly strategy and used as a sorbent for effective trapping of TcO4. Excellent separation of TcO4/ReO4 is demonstrated by fast removal kinetics, good sorption capacity and high distribution coefficient. Remarkably, the most superior selectivity among metal-organic materials reported so far, together with good hydrolytic stability, indicates potential for efficient TcO4 removal. The structure incorporating ReO4 reveals that the supramolecular framework undergoes adaptive reconstruction facilitating the effective accommodation of TcO4/ReO4. The results highlight opportunities for development of soft anion-adaptive sorbents for highly selective anion decontamination.


99Tc, a long-lived (t1/2 = 2.13 × 105 y) radioisotope of technetium, is an abundant and problematic nuclear waste component and potent radioactive pollution source1,2. Complex chemical behavior of 99Tc hampers separation of uranium and plutonium during reprocessing of spent nuclear fuel, and high volatility of 99Tc species (Tc2O7) constrains incorporation into glass waste forms via high-temperature vitrification. 99Tc, as a stable TcO4 in its dominant + 7 oxidation state, is highly water soluble and can migrate readily in the environment, thereby posing severe environmental risks. Therefore, efficient capture of radioactive 99Tc has received considerable attention for both nuclear waste management and contaminant remediation purposes.

Solvent extraction and ion exchange are two well-established effective methods for removal of TcO4 from aqueous media3,4,5,6. In solvent extraction, extractants with anion recognition capability can achieve high selectivity for TcO4− 4,7,8,9, but practical applications are limited by cost and inefficiency. Ion exchange is developed as an alternative of traditional extraction. Despite the ease of implementation and the expected efficient recovery of TcO4 based on ion-exchange method5,10, the total performance of sorbent materials used seems not to be competent. For example, most traditional polymeric materials exhibit slow anion exchange kinetics and poor radiation resistance11,12, while inorganic cationic materials such as layered double hydroxide (LDH)13, sulfides14, and borates15,16 exhibit low sorption capacity and poor selectivity. The emergence of hydrolytically stable cationic metal–organic materials (MOMs) has led to potent applications for capture of oxyanion pollutants3,17,18,19,20. High porosity, structural diversity, and functional tunability21,22,23 render these hybrid materials as promising candidates for TcO4 removal24,25. However, there is still demand for improvement in terms of selectivity of TcO4 sorbents, with enhanced discrimination for TcO4/ReO4 over other anions as a particularly desirable attribute.

There is no doubt that anion receptors7,9,26,27,28,29 of TcO4 have the best ion selectivity. A rational approach for improving the selectivity of solid sorbents is to give sorbent materials an ideal ion-recognition capability by direct functionalization of traditional solid sorbents with covalently attached anion receptors (Fig. 1a)30,31, but unfortunately, chemical modification method generally suffers from the necessity for elaborate syntheses and possible deactivation of functional recognition groups after implanting in bulk materials. Herein, inspired by molecular recognition of anion receptors, we put forward an alternative tactic that circumvents this drawback via an easily prepared anion-adaptive sorbent material that can behave like an anion receptor itself (Fig. 1b)32,33,34,35,36. Conceptually, this soft sorbent material is capable of dynamically tuning the structural arrangement of its framework in response to different anions, enabling attainment of an optimized pore size and shape match for maximum interactions with, and the resulting selectivity for target anions such as TcO4. Specifically, the desirable anion-adaptive sorbent material should have two crucial attributes of structural dynamics and anion-responsive capability, which can be easily achieved in self-organization-based supramolecular materials bearing recognition sites37,38. Glycoluril derivatives containing abundant –CH or –CH2 motifs as potent anion-recognition sites, among which endo-type bambusurils can serve as anion receptors39,40,41, while exo-type cucurbiturils exhibit anion-binding affinity through outer-surface interaction (Fig. 1c), can be used to prepare a class of anion-adaptive cationic materials for specific anion removal42,43,44,45. A multicomponent assembly strategy is proposed for synthesizing such sorbents based on a versatile glycoluril-based macrocyclic host, cucurbit[8]uril (CB8). The CB8 macrocycle used here plays a vital role in accomplishing both the construction of a supramolecular network46,47,48 and anion recognition (Fig. 1d), and endows both important attributes mentioned above: (a) abundant CH and CH2 groups on its waist for outer-surface hydrogen-bonding recognition to promote the TcO4 capture; (b) flexibility of the CB8 encapsulation motif allowing dynamics of the overall supramolecular framework49,50,51.

Fig. 1

Design strategies for introducing anion-adaptive capability to sorbent materials. a Direct modification of organic polymers or metal–organic sorbents with macrocyclic motifs bearing anion-recognition ability (orange lines: backbones of solid sorbents; green circles: anion receptors; purple balls marked as “A”: anions; blue balls marked as “M”: metal nodes). b Supramolecular assembly of smart polymers or metal–organic sorbents exhibiting anion-adaptive behaviors (orange lines: backbones of solid sorbents; green curves: anion-recognition sites; purple circles: anions; blue balls: metal nodes). c Glycoluril-based macrocyclic hosts for anion recognition through two different modes (purple balls: anions). d Dual roles of CB8 in accomplishing both the construction of a supramolecular network by encapsulation and providing outer-surface interaction sites for anion recognition: left, a full view of CB8-based supramolecular framework; right: enlarged diagram of CB8 showing its interactions with the surrounding components (red balls: O atoms; light-blue balls: C atom; dark blue balls: N atoms)

In this work, a CB8-based cationic supramolecular metal–organic framework, SCP-IHEP-1 ([Cu((bpy)2@CB8)(H2O)4](NO3)2·18H2O), is constructed by the supramolecular collaborative assembly. As expected, this material is demonstrated to be an efficient and selective sorbent capable of reversibly sequestrating TcO4/ReO4 by trapping them in specific tetrahedral pores created by CB8 moieties arranged in order. The anion-adaptive capability of this supramolecular sorbent toward effective TcO4 recognition resembles the dynamic behavior of the receptor during ion recognition, and can be taken as a representative TcO4-specific smart sorbent material.


Assembly of SCP-IHEP-1 based on CB8

The cationic supramolecular framework material, SCP-IHEP-1, was synthesized via assembly of CB8, 4,4′-bipyridine (bpy) and Cu(NO3)2 under hydrothermal conditions. It crystallizes in monoclinic space group P21/n (Supplementary Table 1) as pale blue block crystals (Supplementary Figure 1). Crystal structure of SCP-IHEP-1 reveals that all the four components (CB8, bpy, Cu2+, and NO3) (Supplementary Figure 2) are included during the self-assembly process, and the main building unit of the supramolecular framework of SCP-IHEP-1 (Fig. 2a) is a one-dimensional (1D) metal–organic polyrotaxane chain (Fig. 2b) based on encapsulation motif, 2bpy@CB8, linked by Cu2+ (Fig. 1c). Given the potential for competition between metal coordination and supramolecular encapsulation of bpy, one-pot synthesis of SCP-IHEP-1 having both types of connectivities for bpy suggests stepwise assembly, with initial supramolecular encapsulation of bpy in CB8 followed by assembly into a 1D chain via bpy-Cu2+ coordination (Supplementary Figure 3). This assembly mechanism was corroborated by an alternative two-step method in which isolation of the dimeric bpy units encapsulated in CB8, 2bpy@CB8, in the form of [(bpy)2@CB8]0.5·[(bpy)2@CB8]0.5·19H2O (Supplementary Figure 4 and 5) is followed by assembly with the metal ions provided as Cu(NO3)2. It is notable that, whereas 2G@H encapsulation, where G denotes a guest molecule, and H a host, is common for host CB846,47,48,52, this motif is rare for neutral guest such as bpy in CB853. Actually, formation of 2bpy@CB8 in aqueous solution involves a large favorable enthalpy change as a result of release of high-energy water (Supplementary Figure 6 and Supplementary Table 2), which should be taken as the main driving force for this encapsulation54,55 and results in different degrees of pi–pi stacking (Supplementary Figure 4) and a variety of hydrogen bonds between CB8 and bpy (Supplementary Figure 7 and Supplementary Table 3).

Fig. 2

Crystal structure of SCP-IHEP-1. a The cationic supramolecular framework (insert: building blocks of the 1D metal–organic polyrotaxane chain, green macrocycles: cucurbit[8]uril (CB8) molecules; skeletons in orange: 4,4′-bipyridine (bpy); polyhedra in mint green: coordination spheres of copper ion; b the supramolecular assembly motif of 2bpy@CB8; c [Cu(bpy)2(H2O)4]2+ coordination motif; d nitrate-incorporated supramolecular framework of SCP-IHEP-1 (purple: O atom; blue: N atom); e NO3 in a tetrahedral coordination cavity; f proposed stepwise self-assembly process of SCP-IHEP-1 involving four different components

Cationic 1D polyrotaxane chains in SCP-IHEP-1 can further assemble into a three-dimensional (3D) supramolecular framework via cross-linkage of a large number of interchain hydrogen bonds (Supplementary Figure 8 and Supplementary Table 4). The nitrate counterions are located in tetrahedral cavities formed by four neighboring CB8 from the 1D chains (Fig. 2d, e and Supplementary Figure 9), and also contributed a lot to the formation of final supramolecular framework via anion-directed assembly (Fig. 2f). Analysis of the local nitrate anion environment reveals its interaction with only two CB8 macrocycles of the tetrahedral cavity through a limited number of hydrogen bonds (Supplementary Figure 10), suggesting weak interaction with main 1D backbones of SCP-IHEP-1 and the potential for exchange with oxyanions having more favorable interactions, such as TcO4/ReO4.

In contrast, coordination assembly simply from bpy and Cu(NO3)2 in the absence of CB8 macrocycles results in a twofold interpenetrating 3D framework based on six-coordinated copper nodes with deformed octahedral geometry (namely as Cu-bpy, see Supplementary Table 1 and Supplementary Figure 11). In addition to the nitrate directly binding to a copper center, there should be a disordered nitrate anion in the pore of 3D framework to balance the charge.

After exposure of SCP-IHEP-1 crystals for 12 h at 298 K to aqueous solutions with pH values ranging from 3 to 11, the structure as determined by powder X-ray diffraction (PXRD) remained essentially unchanged (Fig. 3a). The results suggest thermal and hydrolytic stability, despite the flexible supramolecular framework. Meanwhile, in contrast to significant dehydration of Cu-bpy at low temperatures (Supplementary Figure 12), SCP-IHEP-1 did not undergo any significant decomposition until over 205 °C (Fig. 3b), suggesting its high thermal stability.

Fig. 3

Hydrolytic stability and thermal stability of SCP-IHEP-1. a PXRD patterns of SCP-IHEP-1 after soaking in aqueous solutions with varying pH values ranging from 3 to 11 for 12 hours at 298 K. b Thermogravimetric analysis (TGA) in air for SCP-IHEP-1

Sorption performance for ReO4 removal

ReO4 was initially used as a nonradioactive structural analog of 99TcO4 to assess anion exchange of SCP-IHEP-1. Batch kinetics experiment shows that removal of ReO4 by SCP-IHEP-1 follows the pseudo-first-order model (Supplementary Figure 13 and Supplementary Table 5), and is achieved to 88% removal at 1 min and to over 95% after 10 min (Fig. 4a). The fast kinetics of ReO4 exchange by SCP-IHEP-1 is superior to those of other cationic metal–organic materials such as SLUG-2120, UiO-66-NH3+17, and Ni(II)-based MOF19, all of which take over 24 h to reach exchange equilibrium for sequestering ReO4. It is notably that, SCP-IHEP-1 also shows faster removal rate and much higher removal ratio than its CB8-free counterpart Cu-bpy (an equilibrium time of 30 min and a final removal ratio of 20%, Supplementary Figure 14 and Supplementary Table 6).

Fig. 4

Performance of SCP-IHEP-1 for ReO4 removal. a Sorption kinetics with that of Cu-bpy used as a comparison; b sorption isotherms with that of Cu-bpy used as a comparison; c effect of pH on the removal percentage of ReO4 (c0 = 44.6 mg L−1, T = 300 K, t = 12 h, V = 8 mL, and m = 4 mg); d effect of competing anions on the ReO4 exchange (c0 = 45.0 mg L−1, t = 12 h, T = 300 K, V = 8 mL, m = 4 mg, and pH = 6.92); e effect of excess NO3 on the ReO4 exchange (c0 = 45.0 mg L−1, t = 12 h, T = 300 K, V = 8 mL, m = 4 mg, and pH = 6.85); f effect of excess SO42− on the ReO4 exchange (c0 = 45.0 mg L−1, t = 12 h, T = 300 K, V = 8 mL, m = 4 mg, and pH = 7.05). Error bars represent the s.d. of uncertainty for each point

As revealed by the sorption isotherm experiment (Fig. 4b), the calculated maximum sorption capacity of SCP-IHEP-1 based on the Langmuir model is 157 mg Re g−1 sorbent corresponding to 211 mg ReO4 g−1 sorbent (Supplementary Figure 15 and Supplementary Table 7), which is higher than those for LDH (130 mg ReO4 g−1)13, NDTB-1 (49 mg ReO4 g−1)15,]16, and UiO-66-NH3+ (159 mg ReO4 g−1)17. Assuming that all the nitrate ions can be exchanged, the sorption capacity of SCP-IHEP-1 for ReO4 observed here reaches to as high as 93% of the theoretical value (226 mg g−1), suggesting its nearly perfect exchange tendency for ReO4. Moreover, the distribution coefficient (Kd) of SCP-IHEP-1 toward ReO4 is 2.6 × 105 mL g−1 (Supplementary Table 8), which is also comparable to recently emerging high-performance cationic MOFs, SCU-100, and SCU-101 (Table 1)24,25, and ensures the decontamination depth of ReO4. In contrast, ReO4 removal by CB8-free Cu-bpy can only achieve a poor separation efficiency (Kd: ~1 × 103 mL g−1, Supplementary Table 8), which is two orders of magnitude lower than that of SCP-IHEP-1. Correspondingly, the derived maximum sorption capacity of 138 mg ReO4 g−1 (Supplementary Figure 16 and Supplementary Table 9) only reaches 14% of the theoretical value (950 mg ReO4 g−1 assuming all the anions could be exchangeable.

Table 1 Comparison of ReO4 removal performance between different cationic materials

In terms of structural reversibility, over 96% of sorbed ReO4 could be exchanged with NO3 in a desorption solution of 0.5 M NaNO3, and the regenerated material retains over 92% of removal percentage after two cycles. The removal percentage of SCP-IHEP-1 for ReO4 keeps at a high level (>96%) within a wide pH range of 4−10 (Fig. 4c) and remains up to 60% at more acidic media with a pH value of 2, revealing a good hydrolytic stability and high separation capability. Studies on the effect of temperature (Supplementary Figure 17) indicates that the present anion exchange may be an exothermic process with an enthalpy change of −25.76 kJ mol−1 (Supplementary Table 10).

Uptake selectivity

Studies on ReO4 exchange selectivity show that SCP-IHEP-1 still selectively removes ReO4 in the presence of one equivalent of several competing anions including NO3, SO42−, CO32−, PO43−, or ClO4 (Fig. 4d). Although ReO4 removal diminishes somewhat when competing with structurally similar ClO4, it remains as high as 91% (Supplementary Table 11). Under similar conditions, ReO4 removal by SCU-10124 does not exceed 90%, and removal by PAF-1-F56 is only ca. 20% in the presence of SO42− or PO43−.

Given the high concentration of nitrate ion in high level nuclear waste stream, the competing effect of excess nitrate anions is critical during TcO4 removal. Moreover, for certain types of nuclear waste, high-concentration SO42− is also another potent competing anions. Therefore, ReO4 removal with higher concentrations of competing NO3 and SO42− were further studied to check the uptake selectivity of ReO4. As shown in Fig. 3e, removal of ReO4 remains as high as 96% for a molar ratio of NO3 to ReO4 of 20:1, and is 84% for a ratio of 100:1 (Supplementary Table 12). Remarkably, an increase in SO42− has little effect on the uptake of ReO4 (Fig. 3f), with removal falling only from 98 to 92% when the SO42−:ReO4 ratio increases from 1:1 to 4000:1 (Supplementary Table 13).

Removal selectivity of SCP-IHEP-1 toward TcO4/ReO4 can be partially ascribed to its inherent feature of inorganic–organic hybrid material based on multi-component collaborative assembly. Generally, anions with higher charge density such as SO42− often have better uptake than those with lower charge density (TcO4/ReO4) during the sorption process with inorganic anion sorbents13,15,16. However, this order always is reversed for organic polymers and inorganic–organic hybrid materials, which is taken as a Hofmeister phenomenon57. This Hofmeister behavior might be originated from the hydrophobic nature of organic backbones of these materials, as evidenced by the methylene/methylidyne-rich tetrahedral pores of SCP-IHEP-1.3 A similar trend is observed for other MOMs bearing local hydrophobic cavities or pores24,25,58. That is to say, considering the differences in hydration energy of anions, the preference for larger poorly hydrated ReO4 anions over NO3 or SO42− reflects the important role of hydration/dehydration in the anion exchange, which is consistent with the exothermic feature of exchange observed above.

TcO4 removal from simulated nuclear wastes

The overall selectivity of SCP-IHEP-1 toward ReO4 against NO3 and SO42− observed here is better than those of MOF-typed (SCU-101)25 and polymeric network-typed (SCU-CPN-1)57 anionic exchange materials with excellent ReO4/TcO4 removal performance emerging recently, making it a promising candidate for selective sequestration of TcO4 from waste solutions, even in the presence of high concentration of competing anions. To assess the potential application of SCP-IHEP-1 in real nuclear solutions containing radioactive TcO4, removal experiments for TcO4 were also tested. Uptake kinetics of TcO4 by SCP-IHEP-1 is as fast as that of ReO4, achieving ~80% removal at 1 min and over 90% after 10 min (Fig. 5), and nearly quantitative removal after 2 h. In a simplified simulated waste stream containing 9.8 ppm 99TcO4 in 0.03 M HNO3 (i.e., a NO3 concentration ~ 500 times higher than TcO4), although the TcO4 removal is affected by the high-concentration competing NO3, the removal percentage of TcO4 is still up to 79.2% using a solid-to-liquid ratio (SLR) of 0.5, which is superior to the removal by SCU-100 (59.3% with a SLR of 1.0)25 and SCU-101 (75.2% with a higher SLR of 10)24 and represents the best removal performance for 99TcO4 among cationic MOMs reported so far.

Fig. 5

Removal of TcO4 as a function of contact time in the absence of competing anion NO3 (blue line; TcO4: NO3 = 1: 0, c0 = 10 mg L−1, V = 40 mL, m = 20 mg, and pH = 7.00) and in the presence of 0.03 M NO3 (green line; TcO4: NO3 = 1: 500, c0 = 10 mg L−1, V = 10 mL, m = 5 mg, and pH = 6.89). Error bars represent the s.d. of uncertainty for each point

Mechanism for selective ReO4 uptake

ReO4 (and by inference TcO4) exchange of SCP-IHEP-1 was monitored by Fourier transform infrared spectroscopy (FTIR) (Fig. 6a), PXRD patterns (Fig. 6b), and energy dispersive X-ray spectroscopy (EDS) (Fig. 6c). Single crystals of ReO4 incorporated material (SCP-IHEP-1-Re) were also obtained and subject to X-ray diffraction structural determination on the Beijing Synchrotron Radiation Facility (BSRF) (Supplementary Figure 18). A comparison of simulated PXRD pattern of crystalline SCP-IHEP-1-Re and actual PXRD of SCP-IHEP-1 after ReO4 exchange (Supplementary Figure 19) confirms that they are totally identical to each other, and crystallographic analysis at the molecular level will be very helpful to understand the recognition mechanism of SCP-IHEP-1 toward ReO4 as well as TcO4. Similarly, ReO4 uptake of Cu-bpy was also evidenced by the signals of ReO4 or Re in FTIR (Supplementary Figure 20) and EDS (Supplementary Figure 21) after exchange experiments. PXRD comparison (Supplementary Figure 22) between Cu-bpy after ReO4 exchange and ReO4 incorporated crystalline analog of Cu-bpy (Supplementary Figure 23) suggests a possible ReO4-induced transformation of Cu-bpy to Cu-bpy-Re along with significant change of Cu2+ coordination sphere and total topological structure, although there might be also a small amount of other undefined products.

Fig. 6

Characterization of SCP-IHEP-1 after ReO4 sorption. a IR spectra of SCP-IHEP-1 before (red) and after (blue) ReO4 exchange; b PXRD patterns before ReO4 sorption (red), after ReO4 sorption (blue) and after material recovery by ReO4 desorption in a solution of 0.5 M NaNO3 (purple); c EDS of SCP-IHEP-1 before (top) and after (bottom) ReO4 exchange; d ReO4 instead of NO3 trapped in a tetrahedral coordination cavity after ReO4 sorption (four adjacent CB8 molecules are shown in different colors and hydrogen atoms in black)

Analysis on the crystal structure of SCP-IHEP-1-Re reveals that ReO4 is trapped in tetrahedral pores surrounded by four adjacent CB8 molecules (Fig. 6d) and fixed by a mass of hydrogen bonds between anion oxygen atoms and outer-surface CH and CH2 groups (a total of 15 such bonds with an average O·H distance of 2.71 Å) (Supplementary Table 3). The crystal structure of SCP-IHEP-1-Re reveals close-packing mode similar to SCP-IHEP-1 but with a change of stacking orientation originated from its single-crystal-to-single-crystal (SCSC) transformation upon ReO4 incorporation (Fig. 7a). Compared to the coordination environment of NO3 in SCP-IHEP-1, encapsulation of ReO4 is achieved by the rearrangement of surrounding CB8 moieties with a resulting slight deformation of the tetrahedral pores (Fig. 7b). The above results indicate that the removal of TcO4/ReO4 by SCP-IHEP-1 is mainly attributed to anion-adaptive reorganization of the CB8-based pores, which can dynamically adapt to the encapsulated anionic guest.

Fig. 7

ReO4 exchange-triggered structural transformation of SCP-IHEP-1. a Single-crystal-to-single-crystal (SCSC) transformation from SCP-IHEP-1 to SCP-IHEP-1-Re upon ReO4 incorporation. b Adaptive structural transformation of CB8-based tetrahedral cavity after encapsulation of ReO4

A comparison of this CB8-based MOM sorbent material with Cu-bpy or other CB8-free MOM sorbents material such as SLUG-2120,41 and SBN58 reveals that the removal of TcO4/ReO4 by SCP-IHEP-1 leads to little structural change of supramolecular framework, while anion removal by the latter ones rely on coordination of target anions with metal centers accompanied by irreversible significant structural arrangement (Supplementary Figure 24). Evidently, the inherent flexibility of soft supramolecular framework of SCP-IHEP-1 facilitates a fast dynamic recognition process, and thus enables superior kinetics as well as good reversibility of anion exchange. Especially, the involvement of CB8 macrocycles in SCP-IHEP-1 plays a vital role in directing supramolecular assembly process, and can be indeed an important contributor to high selectivity in terms of constructing ordered pores for anion trapping and interacting with trapped anions through a mass of hydrogen bonds. The fast kinetics, reversibility and selectivity as well as high efficiency by this type of soft supramolecular material make it outcompetes with traditional cationic MOM sorbents.

In order to understand the driving force underlying the specific ReO4/TcO4 uptake, theoretical calculation methods were used to analyze the interactions of CB8-based host cationic framework with different anions (NO3, ReO4, and TcO4) within SCP-IHEP-1 or SCP-IHEP-1-Re. The GGA-PBE59 functional implemented in VASP 5.460 was used to optimize the unit cells of the crystals, allowing relaxation of all the atom coordinates. With the fully optimized unit cells, three anion-containing tetrahedral pore models based on a simplified host system [H] consisting of the key components of the CB8 macrocycles were built (Supplementary Figure 25). Electrostatic potential (ESP) distribution analysis of these simplified models shows that, the portal carbonyls of CB8 exhibit negative ESP, while the waist CH2/CH groups exhibit positive ESP that facilitates interaction with negative-charged moieties such as NO3 and ReO4 (Supplementary Figure 26 and Supplementary Table 14). Besides the ESP maps, hydrogen bonding orbital interaction analysis from the MO perspective were also studied, and the results reveal that orbital interactions contribute to several hydrogen bonds as evidenced by that of [H] and ReO4 (Supplementary Figure 27).

To further clarify hydrogen bonding interactions between CB8-based host [H] and anions, quantum theory of atoms in molecules (QTAIM) analysis was performed at the B3LYP-D3(BJ)/6-311+G(d,p) level of theory (see Supplementary Methods for details). Several bond critical points (BCPs) between [H] and oxygen atoms of NO3 and ReO4 can be observed (Supplementary Figure 28), indicating noncovalent interactions between CB8-based host [H] and these anions. The parameters of electron density (ρ), Laplacian of electron density (2ρ), kinetic energy density (G), and potential energy density (V) at the representative BCPs are listed in Supplementary Table 15. These values are in the range 0.02 < ρ < 0.07 e/Å3, 0.2 < 2ρ < 0.8 e/Å5, 4.5 < G < 18.3 kJ/mol/Bohr3, −15.7 < V < -3.1 kJ/mol/Bohr3, respectively. For shorter H-Bond lengths (e.g., 2.511 Å), these values are within the scope of weak hydrogen bonding, while the larger ones belong to van der Waals interactions61,62,63. These intermolecular interactions can be further detected by independent gradient model (IGM)64 analysis and reduced density gradient (RDG)65 analysis (Fig. 8 and Supplementary Figure 29 and 30), and proved be weak hydrogen bonding (light-blue area in isosurfaces) and van der Waals interactions (green area in isosurfaces). The results are in excellent agreement with the QTAIM analysis. Besides, the low-density and low-gradient spikes of RDG analysis also confirm the presence of noncovalent interactions (Supplementary Figure 31). In all, the calculation results suggest the vital role of hydrogen bonds in stabilizing the [H]-anion inclusion motifs and thus facilitating the effective accommodation of target anions in the flexible cationic supramolecular framework.

Fig. 8

Intermolecular interactions (isosurfaces: 0.005 a.u.) for different models using IGM analysis. a CB8-based host [H] and NO3; b CB8-based host [H] and ReO4 (blue represents a strong attraction, and red denotes a strong repulsion). All isosurfaces are colored according to a BGR (blue-green-red) scheme over the electron density range −0.05 < sign(λ2)ρ < 0.05 a.u

We computed hydration energies, binding energies and total energies for anion exchange with [H] based on anion-containing tetrahedral pore models built as above (see Supplementary Figure 32). The computed total energies (BEaq) are similar for TcO4 and ReO4, and both of them are larger than that of NO3-[H] model (Supplementary Table 16). Further energy analysis shows that difference of anion-[H] binding energies (ΔBEgas) for all these three models are not significant, whilst the difference of hydration energy (ΔEhyd) between ReO4 and NO3 is dominant. This result suggests the vital role of hydrophobic nature of CB8-based methylene/methylidyne-rich tetrahedral pores of SCP-IHEP-1 in selective TcO4/ReO4 removal, and thus provides a valuable evidence for the Hofmeister bias selectivity of SCP-IHEP-1 mentioned before.


We put forward a tactic using anion-adaptive cationic material with structural dynamics for 99TcO4 sequestration. As a conceptual prototype, a soft supramolecular material, SCP-IHEP-1, was synthesized and has been demonstrated to exhibit excellent removal performance of TcO4 (and ReO4), especially in selectivity against competing anions. This exceptional performance is attributed to the anion-adaptive rearrangement of the CB8-surrounded pores, which can adapt to the encapsulated anionic guest. Hydration energy difference between displaced NO3 and target oxoanions should be the essential driving force for facilitating selective TcO4 uptake of sorbents with hydrophobic pores. The result suggests the potential of this anion-adaptive cationic material SCP-IHEP-1 for effective TcO4 removal, and most importantly, paves a way for developing high efficiency sorbents for anion removal based on soft sorbent materials with anion-adaptive dynamics and efficient anion recognition capability to achieve selective and specific anion binding.



Caution! Tc-99 possesses significant health risks when inhaled or digested and should be handled according to standard precautions and procedures. All Tc-99 studies were conducted in a licensed laboratory dedicated to radiological investigations. Cucurbit[8]uril (CB8) was synthesized according to the previously-reported literature66. 4,4′-bipyridine (bpy), Cu(NO3)2, NH4ReO4, and other reagents were analytically pure and used as received. 99TcO4 stock solutions were prepared by dissolving certain amounts of NH4TcO4 (99%) in deionized water or NO3 solution as desired.

One-pot synthesis of SCP-IHEP-1

An aliquot of 0.2 M Cu(NO3)2 aqueous solution (200 μL, 0.04 mmol) was added to a suspension of 4,4′-bipyridine (bpy) (0.006 g, 0.04 mmol) and CB8 (0.026 g, 0.02 mmol) in water (2 mL) in a stainless-steel vessel. The mixture was sealed, and kept at 150 °C for 48 h. After cooling to room temperature, the obtained blue microcrystals of SCP-IHEP-1 were filtered, rinsed with water and ethanol three times, and dried in air at room temperature. Yield: 0.026 g (59% based on CB8).

Two-step synthesis of SCP-IHEP-1

(a) 2bpy@CB8: 4,4′-bipyridine (bpy) (0.006 g, 0.04 mmol) was added to a suspension of CB8 (0.026 g, 0.02 mmol) in water (2 mL). After incubation in a stainless-steel vessel at 150 °C for 24 h, colorless block crystals of 2bpy@CB8 were obtained in a quantitative yield during cooling to room temperature. The structure of 2bpy@CB8 was confirmed by single-crystal structure determination as [(bpy)2@CB8]0.5·[(bpy)2@CB8]0.5·19H2O (Figure S4) and 1H-NMR spectra (Figure S5). 1H NMR (500 MHz, D2O, δ ppm): 8.49 (m, 8H); 7.42 (m, 8H), 5.84 (d, 16H), 5.52 (s, 16H), 4.22 (d, 16H). (b) SCP-IHEP-1: 0.2 M Cu(NO3)2 aqueous solution (500 μL, 0.04 mmol) was added to a suspension of 2bpy@CB8 intermediate obtained as described above in water (2 mL) in a stainless-steel vessel. The mixture was sealed, and kept at 150 °C for 48 h. After cooling to room temperature, light-blue block crystals of SCP-IHEP-1 were obtained in a high yield (~0.045 g, >99%).

Synthesis of Cu-bpy

An aliquot of 0.2 M Cu(NO3)2 aqueous solution (500 μL, 0.10 mmol) was added to a suspension of 4,4′-bipyridine (bpy) (0.016 g, 0.10 mmol) in water (1.5 mL) in a stainless-steel vessel. The mixture was sealed, and heated slowly to 150 °C in a period of 24 h, and kept at 150 °C for another 48 h. After slowly cooling to room temperature in a period of 24 h, the obtained blue regular plate-like crystals of Cu-bpy were filtered, rinsed with water three times, and dried in air at room temperature. Yield: 0.013 g.

Synthesis of SCP-IHEP-1-Re

To elucidate the exchange and recognition mechanism for SCP-IHEP-1 with ReO4 (and by inference TcO4), crystals of ReO4-incorporated SCP-IHEP-1 sorbent were synthesized through an in situ assembly method. The detailed synthesis procedure is as follows: 0.2 M Cu(NO3)2 aqueous solution (200 μL, 0.04 mmol) and 0.2 M NH4ReO4 aqueous solution (400 μL, 0.04 mmol) was added to a suspension of 2bpy@CB8 obtained as described above in water (2 mL) in a stainless-steel vessel. The mixture was sealed, and kept at 150 °C for 48 h. After cooling to room temperature, small light-blue prismatic crystals of SCP-IHEP-1-Re were obtained. The PXRD pattern of SCP-IHEP-1 after ReO4 uptake collected is fully consistent with the simulated PXRD pattern based on crystal data for SCP-IHEP-1-Re obtained above, suggesting identical structures.

Synthesis of Cu-bpy-Re

An aliquot of 0.2 M Cu(NO3)2 aqueous solution (500 μL, 0.10 mmol) and 0.2 M NH4ReO4 aqueous solution (400 μL, 0.04 mmol) was added to a suspension of 4,4′-bipyridine (bpy) (0.006 g, 0.04 mmol) in water (2.0 mL) in a stainless-steel vessel. The mixture was sealed, and heated slowly to 150 °C in a period of 24 h, and kept at 150 °C for another 48 h. Blue block crystals of Cu-bpy-Re were obtained after slowly cooling to room temperature in a period of 24 h.

X-ray single-crystal structure determination

X-ray diffraction data for SCP-IHEP-1, Cu-bpy, and Cu-bpy-Re were acquired on a Bruker D8 VENTURE X-ray CMOS diffractometer with a Cu Kα X-ray source (λ = 1.54178 Å) at room temperature. Data frames were collected using the program APEX 3 and processed using the program SAINT routine in APEX 3. Data collection for 2bpy@CB8 and SCP-IHEP-1-Re was acquired with synchrotron radiation at Beijing Synchrotron Radiation Facility (BSRF, λ = 0.72 Å) using a MAR CCD detector. The crystal was mounted in nylon loops and cooled in a cold nitrogen-gas stream at 100 K. Data were indexed, integrated and scaled using DENZO and SCALEPACK from the HKL program suite. All crystal structures were solved by means of direct methods and refined with full-matrix least squares on SHELXL-9767, and refined with full-matrix least squares on SHELXL-201467,68. The crystal data of all compounds are given in Supplementary Table 1.

Batch experiments

All the sorption experiments were conducted using the batch sorption method. The solid/liquid ratio performed in all batch experiments was 0.5 g L−1. In a typical experiment, 4 mg of SCP-IHEP-1 or Cu-bpy was added into 8 mL of aqueous solution with a certain concentration of ReO4. The pH values of the solutions were adjusted as required using NaOH and HNO3 and were measured on a digital pH-meter. The mixture was stirred for a specified time (t, min) at a specified temperature (T, K), and separated with a 0.22 μm nylon membrane filter. The concentrations of ReO4 in aqueous solution were determined by inductively coupled plasma optical emission spectrometry (ICP-OES, Horiba JY2000-2).

Data availability

Details for measurements and characterization, detailed experimental procedures, computational methods are given in the Supplementary Methods. The X-ray crystallographic coordinates for structures reported in this study have been deposited in the Cambridge Crystallographic Data Center under accession numbers CCDC: 1874188 (2bpy@CB8), 1874189 (SCP-IHEP-1), 1874190 (SCP-IHEP-1-Re), 1894900 (Cu-bpy), and 1894899 (Cu-bpy-Re), respectively. These data can be obtained free of charge via All data are either provided in the Article and its Supplementary Information or available from the corresponding author upon request.


  1. 1.

    Darab, J. G. & Smith, P. A. Chemistry of technetium and rhenium species during low-level radioactive waste vitrification. Chem. Mater. 8, 1004–1021 (1996).

    CAS  Article  Google Scholar 

  2. 2.

    Popova, Ny. N. et al. Technetium: behaviour during reprocessing of spent nuclear fuel and in environmental objects. Russ. Chem. Rev. 72, 101–121 (2003).

    ADS  CAS  Article  Google Scholar 

  3. 3.

    Custelcean, R. & Moyer, B. A. Anion separation with metal-organic frameworks. Eur. J. Inorg. Chem. 2007, 1321–1340 (2007).

  4. 4.

    Katayev, E. A., Kolesnikov, G. V. & Sessler, J. L. Molecular recognition of pertechnetate and perrhenate. Chem. Soc. Rev. 38, 1572–1586 (2009).

    CAS  Article  Google Scholar 

  5. 5.

    Wilmarth, W. R. et al. Review: waste-pretreatment technologies for remediation of legacy defense nuclear wastes. Solvent Extr. Ion. Exch. 29, 1–48 (2011).

    CAS  Article  Google Scholar 

  6. 6.

    Banerjee, D., Kim, D., Schweiger, M. J., Kruger, A. A. & Thallapally, P. K. Removal of TcO4 ions from solution: materials and future outlook. Chem. Soc. Rev. 45, 2724–2739 (2016).

    CAS  Article  Google Scholar 

  7. 7.

    Alberto, R., Bergamaschi, G., Braband, H., Fox, T. & Amendola, V. 99TcO4 : selective recognition and trapping in aqueous solution. Angew. Chem. Int. Ed. 51, 9772–9776 (2012).

    CAS  Article  Google Scholar 

  8. 8.

    Kubik, S. Anion recognition in aqueous media by cyclopeptides and other synthetic receptors. Acc. Chem. Res. 50, 2870–2878 (2017).

    CAS  Article  Google Scholar 

  9. 9.

    Zhang, D. W., Ronson, T. K., Mosquera, J., Martinez, A. & Nitschke, J. R. Selective anion extraction and recovery using a (Fe4L4)-L-II cage. Angew. Chem. Int. Ed. 57, 3717–3721 (2018).

    CAS  Article  Google Scholar 

  10. 10.

    Burgeson, I. E., Deschane, J. R. & Blanchard, D. L. Removal of technetium from Hanford tank waste supernates. Sep. Sci. Technol. 40, 201–223 (2005).

    CAS  Article  Google Scholar 

  11. 11.

    Davenas, J. et al. Stability of polymers under ionising radiation: the many faces of radiation interactions with polymers. Nucl. Instrum. Meth. B 191, 653–661 (2002).

    ADS  CAS  Article  Google Scholar 

  12. 12.

    Derradji, M. et al. Toward advanced gamma rays radiation resistance and shielding efficiency with phthalonitrile resins and composites. Nucl. Instrum. Meth. B 421, 13–17 (2018).

    ADS  CAS  Article  Google Scholar 

  13. 13.

    Wang, Y. F. & Gao, H. Z. Compositional and structural control on anion sorption capability of layered double hydroxides (LDHs). J. Colloid Interface Sci. 301, 19–26 (2006).

    ADS  CAS  Article  Google Scholar 

  14. 14.

    Neeway, J. J. et al. Removal of TcO4 from representative nuclear waste streams with layered potassium metal sulfide materials. Chem. Mater. 28, 3976–3983 (2016).

    CAS  Article  Google Scholar 

  15. 15.

    Wang, S. A. et al. NDTB-1: a supertetrahedral cationic framework that removes TcO4 from solution. Angew. Chem. Int. Ed. 49, 1057–1060 (2010).

    CAS  Article  Google Scholar 

  16. 16.

    Wang, S. A. et al. Selectivity, kinetics, and efficiency of reversible anion exchange with TcO4 in a supertetrahedral cationic framework. Adv. Funct. Mater. 22, 2241–2250 (2012).

    CAS  Article  Google Scholar 

  17. 17.

    Banerjee, D. et al. Zirconium-based metal-organic framework for removal of perrhenate from water. Inorg. Chem. 55, 8241–8243 (2016).

    CAS  Article  Google Scholar 

  18. 18.

    Colinas, I. R., Silva, R. C. & Oliver, S. R. J. Reversible, selective trapping of perchlorate from water in record capacity by a cationic metal-organic framework. Environ. Sci. Technol. 50, 1949–1954 (2016).

    ADS  CAS  Article  Google Scholar 

  19. 19.

    Desai, A. V., Manna, B., Karmakar, A., Sahu, A. & Ghosh, S. K. A water-stable cationic metal-organic framework as a dual adsorbent of oxoanion pollutants. Angew. Chem. Int. Ed. 55, 7811–7815 (2016).

    CAS  Article  Google Scholar 

  20. 20.

    Fei, H. H., Bresler, M. R. & Oliver, S. R. J. A new paradigm for anion trapping in high capacity and selectivity: crystal-to-crystal transformation of cationic materials. J. Am. Chem. Soc. 133, 11110–11113 (2011).

    CAS  Article  Google Scholar 

  21. 21.

    Eddaoudi, M. et al. Modular chemistry: secondary building units as a basis for the design of highly porous and robust metal-organic carboxylate frameworks. Acc. Chem. Res. 34, 319–330 (2001).

    CAS  Article  Google Scholar 

  22. 22.

    Furukawa, H., Cordova, K. E., O’Keeffe, M. & Yaghi, O. M. The chemistry and applications of metal-organic frameworks. Science 341, 974–988 (2013).

    CAS  Article  Google Scholar 

  23. 23.

    Li, J. R., Sculley, J. & Zhou, H. C. Metal-organic frameworks for separations. Chem. Rev. 112, 869–932 (2012).

    CAS  Article  Google Scholar 

  24. 24.

    Zhu, L. et al. Identifying the recognition site for selective trapping of 99TcO4 in a hydrolytically stable and radiation resistant cationic metal-organic framework. J. Am. Chem. Soc. 139, 14873–14876 (2017).

    CAS  Article  Google Scholar 

  25. 25.

    Sheng, D. P. et al. Efficient and selective uptake of TcO4 by a cationic metal-organic framework material with open Ag + sites. Environ. Sci. Technol. 51, 3471–3479 (2017).

    ADS  CAS  Article  Google Scholar 

  26. 26.

    Amendola, V., Bergamaschi, G., Boiocchi, M., Alberto, R. & Braband, H. Fluorescent sensing of Tc-99 pertechnetate in water. Chem. Sci. 5, 1820–1826 (2014).

    CAS  Article  Google Scholar 

  27. 27.

    Cornes, S. P., Sambrook, M. R. & Beer, P. D. Selective perrhenate recognition in pure water by halogen bonding and hydrogen bonding alpha-cyclodextrin based receptors. Chem. Commun. 53, 3866–3869 (2017).

    CAS  Article  Google Scholar 

  28. 28.

    Ravi, A. et al. Finding a receptor design for selective recognition of perrhenate and pertechnetate: hydrogen vs. halogen bonding. Chem. Commun. 54, 4826–4829 (2018).

    CAS  Article  Google Scholar 

  29. 29.

    Kataev, E. A. et al. Perrhenate and pertechnetate anion recognition properties of cyclo[8]pyrrole. Supramol. Chem. 27, 346–356 (2015).

    CAS  Article  Google Scholar 

  30. 30.

    Alberti, G. et al. Supramolecular receptors in solid phase: developing sensors for anionic radionuclides. Dalton Trans. 42, 6227–6234 (2013).

    CAS  Article  Google Scholar 

  31. 31.

    Ji, X. F. et al. Physical removal of anions from aqueous media by means of a macrocycle-containing polymeric network. J. Am. Chem. Soc. 140, 2777–2780 (2018).

    CAS  Article  Google Scholar 

  32. 32.

    Jung, O. S., Kim, Y. J., Lee, Y. A., Park, J. K. & Chae, H. K. Smart molecular helical springs as tunable receptors. J. Am. Chem. Soc. 122, 9921–9925 (2000).

    CAS  Article  Google Scholar 

  33. 33.

    Kitagawa, S. & Uemura, K. Dynamic porous properties of coordination polymers inspired by hydrogen bonds. Chem. Soc. Rev. 34, 109–119 (2005).

    CAS  Article  Google Scholar 

  34. 34.

    Horike, S., Shimomura, S. & Kitagawa, S. Soft porous crystals. Nat. Chem. 1, 695–704 (2009).

    CAS  Article  Google Scholar 

  35. 35.

    Vanduyfhuys, L. et al. Thermodynamic insight into stimuli-responsive behaviour of soft porous crystals. Nat. Commun. 9, 204 (2018).

    ADS  CAS  Article  Google Scholar 

  36. 36.

    Jie, K. C., Zhou, Y. J., Li, E. R. & Huang, F. H. Nonporous adaptive crystals of pillararenes. Acc. Chem. Res. 51, 2064–2072 (2018).

    CAS  Article  Google Scholar 

  37. 37.

    Lehn, J. M. Toward complex matter: Supramolecular chemistry and self-organization. Proc. Natl Acad. Sci. USA 99, 4763–4768 (2002).

    ADS  CAS  Article  Google Scholar 

  38. 38.

    Aida, T., Meijer, E. W. & Stupp, S. I. Functional supramolecular polymers. Science 335, 813–817 (2012).

    ADS  CAS  Article  Google Scholar 

  39. 39.

    Kaabel, S. et al. Chiral hemicucurbit[8]uril as an anion receptor: selectivity to size, shape and charge distribution. Chem. Sci. 8, 2184–2190 (2017).

    CAS  Article  Google Scholar 

  40. 40.

    Yawer, M. A., Havel, V. & Sindelar, V. A bambusuril macrocycle that binds anions in water with high affinity and selectivity. Angew. Chem. Int. Ed. 54, 276–279 (2015).

    CAS  Article  Google Scholar 

  41. 41.

    Svec, J., Necas, M. & Sindelar, V. Bambus[6]uril. Angew. Chem. Int. Ed. 49, 2378–2381 (2010).

    CAS  Article  Google Scholar 

  42. 42.

    Zhang, M. L., Lin, R. L., Sun, W. Q. & Liu, J. X. Anion encapsulation and complexation by cucurbit[n]urils and their derivatives. J. Incl. Phenom. Macro. 90, 173–187 (2018).

    CAS  Article  Google Scholar 

  43. 43.

    Ni, X. L. et al. Self-assemblies based on the “outer-surface interactions” of cucurbit[n]urils: new opportunities for supramolecular architectures and materials. Acc. Chem. Res. 47, 1386–1395 (2014).

    CAS  Article  Google Scholar 

  44. 44.

    Chen, K. et al. Cucurbit[6]uril-based supramolecular assemblies: possible application in radioactive cesium cation capture. J. Am. Chem. Soc. 136, 16744–16747 (2014).

    CAS  Article  Google Scholar 

  45. 45.

    Liu, L., Jiang, X. A. & Zhang, J. Anion-linked cucurbit[6]uril frameworks formed by microwave-assisted synthesis in ionic liquids. CrystEngcomm 12, 3445–3447 (2010).

    CAS  Article  Google Scholar 

  46. 46.

    Barrow, S. J., Kasera, S., Rowland, M. J., del Barrio, J. & Scherman, O. A. Cucurbituril-based molecular recognition. Chem. Rev. 115, 12320–12406 (2015).

    CAS  Article  Google Scholar 

  47. 47.

    Ko, Y. H., Kim, E., Hwang, I. & Kim, K. Supramolecular assemblies built with host-stabilized charge-transfer interactions. Chem. Commun. 13, 1305–1315 (2007).

  48. 48.

    Kim, H. J. et al. Selective inclusion of a hetero-guest pair in a molecular host: Formation of stable charge-transfer complexes in cucurbit[8]uril. Angew. Chem. Int. Ed. 40, 1526–1529 (2001).

    CAS  Article  Google Scholar 

  49. 49.

    Tian, J., Wang, H., Zhang, D. W., Liu, Y. & Li, Z. T. Supramolecular organic frameworks (SOFs): homogeneous regular 2D and 3D pores in water. Natl. Sci. Rev. 4, 426–436 (2017).

    CAS  Article  Google Scholar 

  50. 50.

    Tian, J. et al. Supramolecular metal-organic frameworks that display high homogeneous and heterogeneous photocatalytic activity for H-2 production. Nat. Commun. 7, 11580 (2016).

    ADS  CAS  Article  Google Scholar 

  51. 51.

    Tian, J. et al. Three-dimensional periodic supramolecular organic framework ion sponge in water and microcrystals. Nat. Commun. 5, 5574 (2014).

    CAS  Article  Google Scholar 

  52. 52.

    Kim, K. et al. Functionalized cucurbiturils and their applications. Chem. Soc. Rev. 36, 267–279 (2007).

    CAS  Article  Google Scholar 

  53. 53.

    Mitkina, T. V., Naumov, D. Y., Kurat’eva, N. V., Gerasko, O. A. & Fedin, V. P. Synthesis and guest exchange reactions of inclusion compounds of cucurbit[8]uril with nickel(II) and copper(II) complexes. Russ. Chem. Bull. 55, 26–35 (2006).

    CAS  Article  Google Scholar 

  54. 54.

    Biedermann, F., Uzunova, V. D., Scherman, O. A., Nau, W. M. & De Simone, A. Release of high-energy water as an essential driving force for the high-affinity binding of cucurbit[n]urils. J. Am. Chem. Soc. 134, 15318–15323 (2012).

    CAS  Article  Google Scholar 

  55. 55.

    Biedermann, F., Vendruscolo, M., Scherman, O. A., De Simone, A. & Nau, W. M. Cucurbit[8]uril and blue-box: high-energy water release overwhelms electrostatic interactions. J. Am. Chem. Soc. 135, 14879–14888 (2013).

    CAS  Article  Google Scholar 

  56. 56.

    Banerjee, D. et al. Removal of pertechnetate-related oxyanions from solution using functionalized hierarchical porous frameworks. Chem. Eur. J. 22, 17581–17584 (2016).

    CAS  Article  Google Scholar 

  57. 57.

    Li, J. et al. 99TcO4 remediation by a cationic polymeric network. Nat. Commun. 9, 3007 (2018).

    ADS  Article  Google Scholar 

  58. 58.

    Zhu, L. et al. Exceptional perrhenate/pertechnetate uptake and subsequent immobilization by a low-dimensional cationic coordination. Polym.: Overcoming Hofmeister Bias Sel. Environ. Sci. Tech. Let. 4, 316–322 (2017).

    CAS  Google Scholar 

  59. 59.

    Perdew, J. P., Burke, K. & Ernzerhof, M. Generalized gradient approximation made simple. Phys. Rev. Lett. 77, 3865–3868 (1996).

    ADS  CAS  Article  Google Scholar 

  60. 60.

    Kresse, G. & Furthmuller, J. Efficient iterative schemes for ab initio total-energy calculations using a plane-wave basis set. Phys. Rev. B 54, 11169–11186 (1996).

    ADS  CAS  Article  Google Scholar 

  61. 61.

    Koch, U. & Popelier, P. L. A. Characterization of C-H-O hydrogen-bonds on the basis of the charge-density. J. Phys. Chem. 99, 9747–9754 (1995).

    CAS  Article  Google Scholar 

  62. 62.

    Espinosa, E., Souhassou, M., Lachekar, H. & Lecomte, C. Topological analysis of the electron density in hydrogen bonds. Acta Crystallogr. B. 55, 563–572 (1999).

    CAS  Article  Google Scholar 

  63. 63.

    Espinosa, E., Alkorta, I., Elguero, J. & Molins, E. From weak to strong interactions: a comprehensive analysis of the topological and energetic properties of the electron density distribution involving X-H center dot center dot center dot F-Y systems. J. Chem. Phys. 117, 5529–5542 (2002).

    ADS  CAS  Article  Google Scholar 

  64. 64.

    Lefebvre, C. et al. Accurately extracting the signature of intermolecular interactions present in the NCI plot of the reduced density gradient versus electron density. Phys. Chem. Chem. Phys. 19, 17928–17936 (2017).

    CAS  Article  Google Scholar 

  65. 65.

    Johnson, E. R. et al. Revealing noncovalent interactions. J. Am. Chem. Soc. 132, 6498–6506 (2010).

    CAS  Article  Google Scholar 

  66. 66.

    Day, A., Arnold, A. P., Blanch, R. J. & Snushall, B. Controlling factors in the synthesis of cucurbituril and its homologues. J. Org. Chem. 66, 8094–8100 (2001).

    CAS  Article  Google Scholar 

  67. 67.

    Sheldrick, G. M. A short history of SHELX. Acta Crystallogr. A 64, 112–122 (2008).

    ADS  CAS  Article  Google Scholar 

  68. 68.

    Sheldrick, G. M. SHELXT—integrated space-group and crystal-structure determination. Acta Crystallogr. A 71, 3–8 (2015).

    Article  Google Scholar 

Download references


We thank the support from the National Natural Science Foundation of China (21671191 and 11405186) and the Major Program of National Natural Science Foundation of China (21790373). The Science Challenge Project (TZ2016004) is also acknowledged. J.G. was supported by the Center for Actinide Science and Technology, an Energy Frontier Research Center funded by the U.S. Department of Energy under Award DE-SC0016568.

Author information




W.Q.S. conceived and supervised the project. L.M. designed and synthesized the material. L.M. and F.Z.L. carried out the uptake experiments and analyzed the data. C.X., H.D., and J.C. performed the Tc-99 experiments. L.M. and K.Q.H. collected and analyzed the crystal data. L.W. performed the TEM-EDS analysis. J.H.L., C.Z.W., and Q.Y.W. performed the modeling and theoretical calculations. L.M., F.Z.L., J.H.L., C.Z.W., and Q.Y.W. wrote the paper. W.Q.S., Z.F.C., and J.K.G. reviewed and edited the paper. All authors discussed the results and commented on the manuscript.

Corresponding author

Correspondence to Wei-qun Shi.

Ethics declarations

Competing interests

The authors declare no competing interests.

Additional information

Journal peer review information: Nature Communications thanks Valeria Amendola and the other anonymous reviewer(s) for their contribution to the peer review of this work.

Publisher’s note: Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Supplementary information

Rights and permissions

Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made. The images or other third party material in this article are included in the article’s Creative Commons license, unless indicated otherwise in a credit line to the material. If material is not included in the article’s Creative Commons license and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this license, visit

Reprints and Permissions

About this article

Verify currency and authenticity via CrossMark

Cite this article

Mei, L., Li, Fz., Lan, Jh. et al. Anion-adaptive crystalline cationic material for 99TcO4 trapping. Nat Commun 10, 1532 (2019).

Download citation

Further reading


By submitting a comment you agree to abide by our Terms and Community Guidelines. If you find something abusive or that does not comply with our terms or guidelines please flag it as inappropriate.


Nature Briefing

Sign up for the Nature Briefing newsletter — what matters in science, free to your inbox daily.

Get the most important science stories of the day, free in your inbox. Sign up for Nature Briefing