Polyacrylonitrile/Crown Ether Composite Nanofibres With High Efficiency for Adsorbing Li(I): Experiments and Theoretical Calculations

Lithium, as the lightest alkali metal, is widely used in military and new energy applications. With the rapid growth in demand for lithium resources, it has become necessary to improve the effectiveness of extraction thereof. By using chemical grafting and electrospinning techniques, nanofibres containing crown ether were developed for adsorbing Li(I) from the brine in salt lakes, so as to selectively adsorb Li(I) on the premise of retaining specific vacancies of epoxy groups in crown ether. In lithium-containing solution, the adsorbing materials can reach adsorption equilibrium within three hours, and the maximum adsorption capacity is 4.8 mg g−1. The adsorption mechanisms of the adsorbing materials for Li(I) were revealed by combining Fourier transform infrared spectroscopy (FT-IR), scanning electron microscopy (SEM), and X-ray photoelectron spectroscopy (XPS) with density functional theory (DFT) calculation. The results indicated that in crown ether, O in epoxy groups was coordinated with Li(I) to form Li–O and four O atoms in the epoxy groups were used as electron donors. After coordination, two O atoms protruded from the plane and formed a tetrahedral structure with Li(I), realising the specific capture of Li(I). By desorbing fibres that adsorbed Li(I) with 0.5-M HCl, the adsorption capacity only decreased by 10.4% after five cycles, proving ability to regenerate such materials. The nanofibres containing crown ether synthesised by chemical grafting and electrospinning have the potential to be used in extracting lithium resources from the brine in salt lakes.


INTRODUCTION
Lithium, as the metal with the lowest density, and has been used in aerospace (Clara and Martins, 2020), medical (Wu and Huang, 2006), and battery (Lee et al., 2018;Wu et al., 2019;Zhang et al., 2019) applications due to its unique physico-chemical properties (Tarascon, 2010). Given the rapid development of portable electronic products and new-energy vehicles, the price of, and demand for, lithium resources have increased sharply in recent years (Xu et al., 2020). According to a United States Geological Survey (USGS) report, 62% of lithium resources in the world are present in brine in salt lakes (Yu et al., 2019). Therefore, it is of economic and strategic significance to extract lithium resources from the brine in salt lakes.
At present, many researchers have reported the recovery of lithium resources from the brine in salt lakes using methods, such as extraction (Torrejos et al., 2016;Shi et al., 2017;Romero et al., 2020), salinity gradient solar ponds (Nie et al., 2011), and adsorption methods (Hong et al., 2018;Bajestani et al., 2019). Due to advantages such as a simple production process (Meshram et al., 2014), low production cost, and low energy consumption (Xu et al., 2016), the adsorption method has attracted increasing attention in the separation and recovery of lithium resources from the brine in salt lakes. Some researchers have synthesised a manganese (Mg)-based adsorbent with spinel structures (H 1.6 Mn 1.6 O 4 , HMn 2 O 4 , and H 4 Mn 5 O 12 ) (Feng et al., 1993;Robinson et al., 2010;Gao et al., 2018;Liu et al., 2020;Qiu et al., 2021), whose maximum adsorption capacity is reported to have reached 40 mg/g; because of specific selectivity of spinel structures for Li(I), metal ions including Li(Ι), Mg(II), Ca(II), K (Ι), and Na(Ι) in the brine in salt lakes are ranked in descending order according to their distribution coefficient K d . Such structures can selectively separate and recover lithium resources from the brine in salt lakes. By using polyvinyl chloride (PVC) as a binder and N-methyl pyrrolidone (NMP) as a solvent,  synthesised granular PVC-H 4 Mn 5 O 12 composites with a diameter of 2-3.5 mm through use of the anti-solvent method. Li(I) diffuses internally in the adsorbent, and the mass transfer coefficient is K f (1.8-2.5) × 10 −5 m/s. Chitraka et al. (2001) used the sol-gel method to synthesise layered H 2 TiO 3 , which is the first ionic sieve type adsorbent adsorbing Li(I) under acidic solution at a pH of 6.5, resulting in an adsorption capacity of 32.6 mg/g. To increase the specific surface area of the adsorbent, some researchers made H 2 TiO 3 into nano-tubes by hydrothermal method (Moazeni et al., 2015). The adsorption capacity increases by 5-10%, and the maximum adsorption capacity reaches 39.43 mg/g. Chen et al. synthesised magnetic Fe 3 O 4 nanoparticles into layered LiCl·2Al(OH) 3 ·nH 2 O (Li/Al-LDHs) to improve separation effects and the recovery rate of the adsorbing materials from the brine in salt lakes. Moreover, the layered structures of the adsorbing materials were characterised by the quantitative method, thus proving their stability. Although the adsorption capacity of the synthesised magnetic Li/Al-LDHs decreases from 5.83 to 3.46 mg/g, the recovery rate of the adsorbing materials reaches 97%, which improves the efficiency of recovering lithium resources from salt lakes (Chen et al., 2020). Based on the above reports, researchers have studied the stability, adsorption capacity, and recovery of adsorbents, but these adsorbents are particles or powders, which are difficult to recover and have poor permeability in the adsorption process. In actual production, granular adsorbents can be crushed under extrusion and therefore difficult to recover, becoming a bottleneck restricting the industrial application of the adsorption method. This makes it necessary to develop an adsorbing material with good permeability, a high recovery rate, and easy separation in the later stages of processing.
Fibre-based adsorbing materials are ideal adsorbing materials with the advantages of high porosity, large specific surface area, and good internal pore connectivity. By combining the electrospinning method with in-situ polymerisation, Wang et al. (2013) prepared polyacrylonitrile/polypyrrole (PAN/PPy) composite nanofibres with core-shell structures to remove Cr(VI) in aqueous solution. The presence of PPy layers on the surface of PAN nanofibres was confirmed by attenuated total reflection-Fourier transform infrared (ATR-FTIR) spectroscopy and X-ray photoelectron spectroscopy (XPS). The materials have good selectivity for Cr(VI) in water. With the decrease of initial pH of the solution, the adsorption capacity increases. When the initial concentration of Cr(VI) in the solution is 200 mg/L, adsorption equilibrium can be reached in 90 min. Deng et al. (2016) synthesised a novel polyacrylonitrile-based fibre modified with thiosemicarbazide (PANMW-TSC) under microwave irradiation and studied the adsorption of the materials for Cd(II) and Pb(II) in aqueous solution. The adsorption capacities separately reach 165.3 and 186.2 mg/g, indicating that the materials effectively adsorb Cd(II) and Pb(II) in wastewater. Choi et al. (2017) synthesised polyethylenimine (PEI)/polyvinyl chloride (PVC)-crosslinked fibre (PEI/PVC-CF) by utilising PEI and PVC as raw materials. The maximum adsorption capacity of the materials for Pd(II) in acidic solution is 146.03 mg/g and after five adsorption cycles, the adsorption capacity remains unchanged. This indicates that the fibrebased adsorbing materials have stable structures and good application prospects. As far as we know, there are few reports on the selective separation of Li(I) from salt lakes based on fibrebased adsorbing materials. This research intended to synthesise nano-sized adsorbing materials by grafting 2-methylol-12crown-4 (2M12C4) onto nano-SiO 2 by chemical grafting and electrospinning. Moreover, the materials were used for selective separation of Li(I) from the brine in salt lakes.
In the present study, γ-glycidoxypropyltrimethoxysilane (KH560) was used as a coupling agent and 2MI12C4 was grafted onto nano-SiO 2 to synthesise nano-sized adsorbing materials. Furthermore, the nanoparticles were blended into polyacrylonitrile to prepare nanofibres by electrospinning. The materials are new adsorbent materials with low costs, good hydrodynamic properties, and they can be easily separated from solution. The internal structure, stability, and directional capture mechanisms of the adsorbing materials for Li(I) were revealed based on a series of characterisations, adsorption experiments, and theoretical calculations. The results demonstrate that the materials have the potential to be used in the separation and recovery of lithium resources from the brine in salt lakes.

Materials and Chemicals
The necessary chemical reagents (analytically pure) were mainly purchased from Sinopharm Chemical Reagent Co., Ltd. and Rhawn Reagent Co., Ltd. Detailed information about the reagents was provided in Supporting Material (Supplementary Text S1). The brine was sampled from Zabuye Salt Lake in Tibet Autonomous Region, China and its pH was 8.4. The concentrations of each element were measured by inductively coupled plasma-atomic emission spectroscopy (ICP-AES). The results are summarised in Supporting Material (Supplementary Table S1).
Synthesis of 2-Hydroxymethyl-12-crown-4@ SiO 2 Nanofibres (PAN-CE@SiO 2 ) SiO 2 with a mass of 1 g and KH560 (also 1 g) could be added to a toluene solution (50 ml) for refluxing for 24 h. The solid products were thrice-washed with deionised, then placed in a vacuum oven at 65°C and dried for 12 h. Furthermore, 1 g of the dried solid product, 45 ml trichloromethane (CHCl 3 ), and 1 ml 2M12C4, were simultaneously added to a three-necked flask with a volume of 100 ml and then 2 ml trifluoroacetic acid (CF 3 COOH) was added as a catalyst. The solution was stirred for 7 h at a constant temperature of 45°C, thus obtaining CE@SiO 2 after vacuum filtration.
The pre-treated CE@SiO 2 nanopowder (0.5 g) was added to N, N-dimethylformamide for ultrasonic dispersion for 30 min and then PAN fibres were added. The uniform and transparent spinning solution with the concentration of 13 wt% was prepared through magnetic stirring at 90°C for 4 h. The spinning solution was poured into a 10 ml needle syringe with a 18G needle as the spinning head, whose inner diameter was 0.83 mm. After that, the syringe was installed on a micropump for controlling the flow rate of spinning solution. The specific spinning parameters are displayed as follows: the voltage of 15 kV and the flow rate of spinning solution of 0.25 ml/min. Moreover, a drum receiver was rotated at 450 rpm and the receiving distance was 150 mm. The PAN-CE@SiO 2 nanofibres were obtained through vacuum drying of the spinning products in an oven at 45°C for 12 h (Figure 1).

Characterisation
The samples in each stage of PAN-CE@SiO 2 synthesis were characterised by utilising techniques, such as scanning electron microscopy (SEM), XPS, and Fourier transform infrared (FT-IR) spectroscopy. The concentrations of ions in the solution were determined by the ICP-AES method. The detailed characterisation information is illustrated in Supporting Material (Supplementary Text S3).

Adsorption Experiment
Experiments, such as static adsorption, adsorption selectivity, adsorption kinetics, adsorption isotherms, and cyclic performance were conducted on the adsorbing materials. The data pertaining to the adsorption kinetics were analysed by pseudo-first-order and pseudo-second-order models: data pertaining to the adsorption isotherms were fitted with Langmuir and Freundlich models. Li(I) desorption and recycling performances were studied by using the fixed-bed adsorption method to investigate the ease of regeneration of the adsorbing materials. A series of experiments were conducted on the selective adsorption of the materials for ions from the brine, and the details are shown in Supporting Information (Supplementary Text S3).

Calculation Methods
The adsorption mechanisms of PAN-CE@SiO 2 for Li(Ι) were further calculated based on the density functional theory (DFT): all calculations were conducted by utilising Gaussian 09 software. The B3LYP (Ramos-Sanchez et al., 2013;Zhu et al., 2019) hybrid functional is very reliable in dealing with electron exchange and correlation in a wide range of molecular systems, the initial structure of PAN-CE@SiO 2 and Li(Ι) composites was optimised by 6-31+G (d, p) basis sets of the B3LYP hybrid functional. In addition, the natural bond orbit (NBO) of the composites was calculated by using 6-31+G (d, p)  basis sets of the B3LYP hybrid functional, which allowed

RESULTS AND DISCUSSION
Characterisation of PAN-CE@SiO 2 In Figure 2A, regular nanofibres have uniformly distributed diameters of about 330 nm and smooth surfaces, and a large number of pores are distributed between fibres, which are conducive to capture (by PAN-CE@SiO 2 ) of target ions from the brine. Infrared spectra of activated SiO 2 as well as CE@ SiO 2 before and after adsorbing Li(I) are displayed in Figure 3. In all samples, absorption peaks attributed to-O-, C C and Si-O stretching vibrations can be observed at 1,140 (Kong et al., 2004), 1,640, and 479 cm −1 (Zhong et al., 2021), respectively. After chemical grafting, an absorption peak attributed to the stretching vibration of epoxy groups in 2M12C4 is found at 590 cm −1 and the absorption peak assigned to the C-H stretching vibration in 2M12C4 appears at 2,875 cm −1 . Moreover, the absorption peak at 3,525 cm −1 is assigned to O-H stretching vibration in 2M12C4. The characteristic absorption peak of-O-at 1,140 cm −1 is significantly enhanced and becomes wider and sharper (Sileika et al., 2011;Salih et al., 2015),   suggesting that the chemical reaction used to prepare nanofibres by grafting 2M12C4 onto the activated SiO 2 had succeeded.

Effects of pH on Adsorption
The pH value is an important factor affecting the adsorption for metal ions, because it can change the forms of metal ions in aqueous solution and the number of charges on the surface of the adsorbing materials. As displayed in Figure 4, the effects of PAN-CE@SiO 2 with changing pH value in the range of 2-10 on the adsorption capacity for Li(I) were evaluated (because the asprepared materials can be damaged at other pH values). Figure 4 demonstrates that the adsorption capacity gradually increases when the pH is increased from 2.0 to 6.0. When the pH value is about 6.0, the adsorption capacity for Li(I) reaches the maximum and is 4.8 mg/g; as the pH value is increased beyond 6.0, the adsorption capacity begins to decrease. The reason for this is as follows: when the pH value is low, there is much free H + in the solution and functional groups can be protonated. Moreover, O in epoxy groups binds with H + , so the number of binding sites on Li(I) decrease. Therefore, the adsorption capacity gradually decreases when the pH value is less than 6.0. As the pH value is increased beyond 6.0, the concentration of OH − in the solution increases, which may cause some Li(I) in the solution to be present in the form of [Li(OH) 2 ] -, thus affecting coordination between O-in epoxy groups in PAN-CE@SiO 2 and Li(I). Therefore, the adsorption capacity gradually decreases when the pH value exceeds 6.0. Figure 5 show the changes in adsorption of the adsorbent for Li(I) with time: there is a rapid adsorption of Li(I) by the adsorbent. The adsorption rate for Li(I) exceeds 90% at about 2 h and the whole adsorption process can reach basic equilibrium within 3 h. This may be because rings of epoxy groups in PAN-CE@SiO 2 are opened to form a C-O-structure, which adsorbs Li(I). The decrease of the adsorption rate in the later stage may be due to the reduction of the C-O-structure without coordination with Li(I) and the concentration of free Li(I) in the solution, so that the adsorption rate decreases. In the preparation of the adsorbent, epoxy groups in crown ether are specific vacancies for Li(I) adsorption. These adsorption sites are usually located deeper in the adsorbing materials, and the rings cannot be opened unless eluted with dilute HCl, however, Li(I) is migrated inwards only by molecular diffusion, resulting in a longer time to reach overall adsorption equilibrium.

Adsorption Behaviours
The better to reveal adsorption mechanisms of PAN-CE@SiO 2 for Li(I), the experimental data were analysed by using two common kinetic models (the pseudo-first-order and pseudosecond-order kinetic models). Table 1 lists relevant kinetic parameters, while the fitting curve of kinetics is shown in Supplementary Figure S1. Based on kinetic data, the pseudosecond-order kinetic model is better suited to describing the whole adsorption process (the correlation coefficient reaches 0.998). The maximum equilibrium adsorption capacity calculated through the pseudo-second-order kinetics is closer to the experimental data, so it can be considered that this is a chemical adsorption process. As expected, it is the presence of epoxy groups in PAN-CE@SiO 2 that provides the C-Ostructure, which determines the amount of Li(I) bound thereto. In the preparation of the adsorbent, the vacancies for Li(I) adsorption reside in epoxy groups between PAN-CE@SiO 2 layers and the diffusion of Li(I) between PAN-CE@SiO 2 layers is the dominant factor governing the whole adsorption process. Therefore, through a certain temperature rise or proper stirring, the overall adsorption process can be accelerated.
The adsorption isotherms are illustrated in Figure 6: with the increase of the initial concentration, the equilibrium adsorption capacity of the adsorbing materials for Li(I) rises. As the concentration of Li(I) in the system rises, the driving force for mass transfer increases. As mentioned above, the adsorption sites for Li(I) in the prepared adsorbing materials are from epoxy groups in crown ether grafted onto SiO 2 during preparation, so the number of adsorption sites for Li(I) in the adsorbent is fixed. When the adsorption sites in epoxy groups are largely all occupied by Li(I), the adsorption capacity will not change to any significant extent thereafter.
In this study, the experimental data were fitted by Freundlich and Langmuir adsorption isotherm models and the relevant data are listed in Table 2. It can be found that the correlation coefficient fitted by the Langmuir adsorption isotherm model is closer to 1 and the calculated maximum adsorption capacity is closer to the measured adsorption capacity, suggesting that the adsorption process is more consistent with the Langmuir adsorption isotherm model and the adsorption process entailed monolayer adsorption. The reason for this is as  follows: the number of effective adsorption sites for Li(I) is fixed during preparation of the adsorbent. Moreover, there is a certain space between these vacancies for Li(I) adsorption, while there is no interaction between the vacancies for adsorption. Compared with lithium-adsorbing materials reported in recent studies, the PAN-CE@SiO 2 used in the present study exhibits a faster adsorption rate (Table 3) and can reach adsorption equilibrium in 3 h. This suggests that the adsorption sites of PAN-CE@SiO 2 are easier to identify, which imparts excellent adsorption kinetics to the material.

Selectivity and Ability to be Regenerated
The selectivity and ability to be regenerated of the adsorbing materials are important factors determining whether the adsorbing materials can be industrialised or not. Owing to Li(I) being generally associated with Mg(II), Na(Ι), Ca(II), and K(Ι) in the brine in a salt lake, these four metal ions were selected to investigate the selectivity of the adsorbing materials for Li(I). Figure 7 demonstrates the competitive adsorption results of PAN-CE@SiO 2 for ions in solution at pH values of 3, 6, and 9 and Table 4 lists relevant selectivity parameters. It can be found from Figure 7 that the adsorption capacity of the adsorbing   materials for Li(I) in the mixed solution is much greater than those for the other metal ions and Li(Ι), Mg(II), Na(Ι), Ca(II), and K(Ι) are ranked thus in descending order according to competitive adsorption. When the pH value is 6, the adsorption capacities of each ion are maximised. This may be because free H + under acidic conditions at a pH value of 3 can bind with more C-O-, thus reducing the number of effective adsorption sites in epoxy groups. Under alkaline conditions at a pH value of 9, the OH − concentration in the solution is high and many complex ions are produced, influencing binding between C-O-and metal ions. It is evident that PAN-CE@SiO 2 has a certain affinity to Mg(II), probably because vacancies in epoxy groups of crown ether are matched with the diameter of Li(I), while the radius (0.065 nm) of Mg(II) is close to that (0.068 nm) of Li(I). Therefore, PAN-CE@SiO 2 can adsorb a certain amount of Mg(II). For PAN-CE@SiO 2 reaching saturated adsorption, Li(Ι) can be eluted with 0.5-M HCl. After five adsorption-desorption cycles in the solution with the pH value of 6, PAN-CE@SiO 2 still maintains its good adsorption performance and selectivity for Li(I) (Figure 8) and the adsorption capacity reaches 4.3 mg/g. The selectivity coefficients for Mg(II), Na(Ι), K(Ι), and Ca(II) are 8.47, 18.30, 39.01, and 31.38, respectively. Therefore, the prepared adsorbing materials have good stability and broad application prospects.

Adsorption Mechanisms
The adsorption mechanisms for Li(I) on the surface of PAN-CE@ SiO 2 were revealed from a macroscopic perspective through an adsorption experiment. By means of XPS, FT-IR spectroscopy, and theoretical calculation, the capture mechanisms of adsorption sites for Li(I) were further explained from a microscopic perspective. The relevant adsorption mechanisms are shown in Figure 9. Figure 3 compares infrared spectra of the adsorbent before and after adsorbing Li(I). The absorption peak assigned to C-H stretching vibration in 2M12C4 migrates from 2,875 cm −1 on the CE@SiO 2 curve to 2,890 cm −1 on the CE@SiO 2 -Li(I) curve. The absorption peak ascribed to stretching vibration of epoxy groups in 2M12C4 at 590 cm −1 on the CE@SiO 2 curve migrates to 770 cm −1 on the CE@SiO 2 -Li(I) curve. This is probably because more energy is required for vibration of bound metal ions. In addition, several studies show that this is caused by adsorption of N-and O-containing functional groups for metal ions. Figure 2B shows an SEM micrograph after adsorption of Li(I): compared with the SEM image before adsorption, the diameter of nanofibres increases and the surface becomes rougher after adsorption. The reason for this may be that the volume of epoxy groups in PAN-CE@SiO 2 increases after adsorption of Li(I) and the introduction of Li(I) makes the surface of the adsorbent rougher. Figure 10 shows fullspectrum fitting 1) and narrow-spectrum fitting 2) of XPS before and after the adsorption of PAN-CE@SiO 2 for Li(I). On the curve after Li(I) adsorption in Figure 10A, in addition to the original elements, an obvious characteristic peak corresponding to the presence of lithium appears at 55.84 eV. The right-shift of the main peak indicates that Li(I) has been coordinated with adsorption sites in PAN-CE@SiO 2 . Besides, Figure 10B illustrates the peak fitting of C-O before and after the adsorption for Li(I). After the adsorption, The adsorption mechanisms of PAN-CE@SiO 2 for Li(I) were explored by way of DFT calculation. Figure 11 shows the optimal structures before and after surface functional groups bind with   Table S3). It is found that four O atoms in functional epoxy groups in 2M12C4 simultaneously bind with Li(I) to form a tetrahedral structure and Li(I) is located above the crown ether ring. As listed in Table 5, after coordination with Li(I), and the bond angles of two C-O-C in the functional epoxy groups of 2M12C4 decrease from 118.29 eV (117.15 eV) to 117.25 eV (115.07 eV) in terms of the binding energy, respectively. This is because the minimum cavity size in the complex of 2M12C4 and Li(I) is 3.44 Å, which is much smaller than the sum (4.32 Å) of the ion diameters of Li(I) and O 2− . Therefore, during coordination, the vacancies in functional epoxy groups in 2M12C4 cannot hold Li(I), and two O atoms bend out of the plane to bind with Li(I).
Through NBO, the mechanisms of action between functional groups and metal ions were further analysed and salient calculation parameters are listed in Table 5. The binding energy of Li(I) complex is −232.18 kcal/mol, indicating a strong affinity of PAN-CE@SiO 2 to Li(I). Furthermore, the analysis of NBO partial charge shows that the charge of Li(I) is 0.755, while that of the ligand is 0.245. This result suggests that there is charge transfer between surface functional groups and metal ions in the process of adsorption. As shown in Table 5, the natural layout of electrons of Li(I) is expressed as 2s 0.08 3p 0.16 3d 0.01 , indicating that electrons are mainly transferred from functional groups to the 3p orbit of Li(I). This is also consistent with the fitting results of XPS in Figure 11, that is, C-O-in epoxy groups of PAN-CE@SiO 2 (as an electron donor) is involved in the coordination of Li(I). Figure 12 compares the highest occupied molecular orbitals (HOMOs) and lowest unoccupied molecular orbitals (LUMOs) before and after the adsorption of PAN-CE@SiO 2 for Li(I). It can be observed from the figure that the HOMOs before the adsorption of PAN-CE@SiO 2 are mainly distributed on epoxy groups of 2M12C4, while they are mainly found on three O atoms and adjacent C and H atoms in epoxy groups of 2M12C4 after the adsorption process. Before the adsorption of PAN-CE@SiO 2 , the LUMOs are almost distributed throughout the whole functional group, and after adsorption of Li(I), they are mainly shown on C, H, and O atoms (other than epoxy groups), further evincing the electron transfer between ligand and metal ions during the adsorption process. Meanwhile, according to second-order Moller-Plesset perturbation theory, the stabilisation energy E (2) reflects the degree of delocalisation of electrons. The stabilisation energy E (2) of this metal complex was calculated ( Table 2): the stabilisation energies E (2) of LP(O10)-LP*(Li), LP(O11)-LP*(Li), LP(O18)-LP*(Li), and LP(O25)-LP*(Li)) of Li(I) are 14.30, 12.04, 12.53, and 14.29 kcal/mol, respectively. This further verifies that PAN-CE@SiO 2 mainly depends on the electron transfer between the four O atoms in epoxy groups of 2M12C4 and Li(I) to produce coordination and form a stable complex, thus achieving the purpose of adsorption. This also corresponds to XPS and FT-IR results, that is, the four O atoms in epoxy groups (as electron donors) coordinate with Li(I), to adsorb Li(I).

CONCLUSION
A new type of complex nanofibre, namely adsorbing material PAN-CE@SiO 2 , was developed by grafting 2M12C4 onto activated SiO 2 and applied to the brine in a salt lake to adsorb Li(I) in a selective manner. A series of characterisation and adsorption experiments on PAN-CE@SiO 2 were conducted. The results show that the selectivity coefficients of PAN-CE@SiO 2 for Mg(II), Na(Ι), K(Ι), and Ca(II) in the mixed solution with the pH value of 6 are, separately, 8.47, 18.30, 39.00, and 31.38, proving that PAN-CE@SiO 2 can selectively adsorb Li(I). When the pH value is 6, the adsorption capacity is maximised at 4.8 mg/g. The adsorption kinetics confirms to the pseudo-second-order model, while the isothermal adsorption model is in line with the Langmuir model. The adsorption process is one of chemical adsorption. The directional selective adsorption mechanisms of the adsorbing materials for Li(I) were revealed by combining FT-IR, SEM, and XPS with DFT calculation. After five cyclic adsorption-desorption experiments, the adsorption capacity remains at 4.3 mg/g, indicating that PAN-CE@SiO 2 has good stability and can be regenerated. PAN-CE@SiO 2 can be used to separate and recover lithium resources from the brine in a salt-lake, so making it a promising new adsorbing material with the potential for industrial application.

DATA AVAILABILITY STATEMENT
The original contributions presented in the study are included in the article/Supplementary Material, further inquiries can be directed to the corresponding authors.