Abstract
Tetrabromobisphenol A (TBBPA) has been considered as one of the persistent organic pollutants in water. It is urgent to determine TBBPA in environment due to its detriment to humans and aquatic species. However, sample pretreatment prior to instrumental analysis is always required because of the low concentration of TBBPA and the complexity of the matrix. A novel molecularly imprinted polymer (MIP) was prepared using magnetic mesoporous TiO2 as matrix. The mesoporous TiO2 layer could provide sufficient recognition sites for MIP, and Fe3O4 core can facilitate its separations from liquid medium. After azido was introduced onto Fe3O4@mTiO2 by non-covalent effect, alkynyl-terminated reversible addition − fragmentation chain transfer (RAFT) agent was fixed by click chemistry. The MIP was prepared via RAFT polymerization in the presence of TBBPA using 4-vinylpyridine (4-VP) and ethyleneglycol dimethacrylate (EGDMA) as functional monomer and crosslinker, respectively. The adsorption process reached equilibrium within 20 min. The maximum adsorption capacity of MIP for TBBPA at an ideal ratio of 4-VP and EGDMA was 41.67 mg g−1 and was much higher than that of non-imprinted polymer (20.92 mg g−1). The MIP also exhibits excellent affinity towards TBBPA in the presence of structural analogs. Additionally, the as-prepared MIP can be repeatedly reused due to the magnetic core.
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1 Introduction
Brominated flame retardant (BFR) has been widely used in plastics and textiles such as electronics, furniture, and clothing [1]. TBBPA, as one of the most ordinary BFR is mostly used as a reactive component in phenolic resins and polycarbonate. Lower grades of TBBPA are also used in epoxy for printed circuit boards, which means that it is incorporated into the polymer backbone [2]. However, as a persistent toxic environmental pollutant and already detected in sewage, sediment, wildlife, and human serum, TBBPA has adverse effects on nature and the human health [3, 4]. Recent researches have also shown that the relative venomous of TBBPA shows a greater potency than its derivatives [5]. The detection of the TBBPA in various matrices has attracted international attention in the last few years.
Based on gas chromatography or high-performance liquid chromatography (HPLC) and other related technologies, sensitive and reliable methods such as liquid chromatography tandem mass spectrometry, gas chromatography-electron capture negative ionization mass spectrometry, and gas chromatography tandem mass spectrometry solid-phase extraction have been developed for the detection of tracing TBBPA [6, 7]. Sample processing procedures prior to instrumental analysis are often critically required, because of the entanglement of the environmental matrix and the low concentration of TBBPA.
Molecularly imprinted polymers exhibit excellent affinity towards target molecule because of the presence of the cavity that matches well with the size and force between the target molecule [8]. Therefore, MIP was commonly used for catalysis, separation, solid-phase extraction, and sensing [9, 10]. Applying molecular imprinting techniques to detect TBBPA will be very promising because of its powerful molecular recognition capabilities [11]. However, conventional methods for preparing molecular polymer based on bulk polymerization or precipitation polymerization have some inconveniences, such as the leakage of the template and the incorporation of the binding cavity deeply into the polymer matrix result in the template being difficult to elute, fewer recognition sites, and poor accessibility, which in turn exhibits poor imprinting effect [12].
The surface molecularly imprinted polymer can effectively avoid the above shortcomings of imprinted polymer obtained by the conventional polymerization method because its recognition site is immobilized on the exterior of the carrier. The recognition site and the binding cavity are only locked on the surface of the polymer, which improves the accessibility of the recognition site and the mass transfer rate and enhances the efficiency of the imprinting [13]. Generally, polystyrene nanoparticles, silica nanoparticles, and magnetic ferro ferric oxide nanoparticles are used as support for MIP layer [14,15,16,17].
Among many selectable carriers, magnetic nanoparticles have the most potential for application. Their outstanding advantages enable the imprint material to be quickly and efficiently isolated by an external magnetic field without other complicated operations [18]. However, magnetic nanoparticles are easy to be oxidized and unstable in acidic environments, and it is generally required to functionalize them to prepare core–shell imprinted polymers conveniently.
The mesostructured support should be the optimum choice in terms of effectively reducing the response time and increasing the sensitivity of the imprinted polymer due to its well-defined channel structure. The well-organized pore structure allows it to have higher specific surface area, thereby possessing more binding sites and improving the binding ability of the imprinted material [19]. Mesoporous silica and metal organic framework were conventional choice owing to their adjustable pore structure [20, 21]. Xie et al. prepared molecularly imprinted polymer using magnetic mesoporous silica as supports, and the obtained imprinted polymer exhibited excellent performance for detecting protocatechuic acid. The maximum adsorption capacity was 2.3 times than the imprinted material prepared using non-porous supports under the same conditions [21]. The results inform that mesoporous support can effectively improve the recognition properties of as-prepared imprinted polymer and it could be an ideal support for surface imprinted polymer.
The chain transfer reaction is inevitable in the conventional radical polymerization system which resulted in the decreased polymerization degree and the uncontrollable structure of the obtained polymer. Controlled/living radical polymerization (CLRP) can overcome the disadvantages of traditional free radical polymerization and can better control the molecular structure. As one of the most used CLRP, the RAFT polymerization can not only maintain a narrow molecular weight distribution and a mild polymerize conditions, but also no metal ions residue in the polymer matrix. More importantly, it provides a convenient approach for later modification of as-prepared MIP by subsequent polymerization using another functional monomer which will broaden the application filed of MIP [22]. Benefiting from the advantages that mentioned above, RAFT polymerization was used to prepare multifunctional MIP as an attractive approach [23, 24].
In this study, the advantages of magnetic nanospheres, mesoporous supports, and RAFT polymerization were combined to prepare TBBPA imprinted MIP for efficiently detect TBBPA. To the best of our knowledge, TBBPA-related MIP was generally prepared by sol–gel method in the previous work, construction of TBBPA imprinted MIP based on combining the advantages of RAFT polymerization, and magnetic mesoporous support has never been reported [1, 5]. Magnetic mesoporous nanoparticles were firstly prepared using Fe3O4 as core, non-porous SiO2 as inner protecting layer and mesoporous TiO2 as outer layer which will provide sufficient recognition site for MIP. Azido was then introduced by a versatile no-covalent approach using azido-functionalized dopamine, and alkynyl-terminated RAFT agent was introduced by click chemistry between alkynyl and azido. TBBPA imprinted MIP was finally prepared by RAFT polymerization using 4-vinyl pyridine, ethyleneglycol dimethacrylate, and TBBPA as functional monomer, crosslinker, and template molecule, respectively. Both the morphology and structure of the obtained MIP was characterized. The specific recognition property was measured by adsorption isotherms, adsorption kinetics, selectivity experiments, and competitive binding assay. The results designated that as-prepared MIP exhibited excellent specific recognition properties for TBBPA and it has potential to be used for detection of TBBPA in complicated environment.
2 Experimental
2.1 Materials
Sodium acetate, 2,2-azobisisobutyronitrile (AIBN), and trisodium citrate dihydrate were supplied by the Guangfu Chemical Industry (Tianjin, China). Ethanol, methanol, dichloromethane (CH2Cl2), ethyl acetate, dimethyl sulfoxide (DMSO), ethylene glycol, and acetic acid were supplied by the Guanghua Chemical Industry (Guangdong, China). Sodium azide (NaN3), toluene, ferric chloride (FeCl3), tetraethyl orthosilicate (TEOS), ammonium hydroxide (NH3·H2O), tetrabutyl titanate (TBOT), and CuSO4·5H2O were supplied by the Sinopharm Chemical Reagent Co. (Shanghai, China). L-ascorbic acid sodium, 3-bromo-1-propanol, glutaric anhydride, bisphenol A (BPA), N, N'-dicyclohexylcarbodiimide (DCC), 3-hydroxytyramine hydrochloride, ethyleneglycol dimethacrylate (EGDMA), 4,4'-dihydroxybiphenyl (BIP), 4-vinyl pyridine (4-VP), tetrabromobisphenol A (TBBPA), 4-t-butylphenol (BP), and 4-dimethylaminopyridine (DMAP) were provided by Energy Chemical Industry Co. Ltd. (Shanghai, China). Azido-functionalized dopamine is synthesized in keeping with the literature, and the 1H NMR spectrum is presented in Figs. S1–S4 [25, 26].
2.2 Synthesis of Fe3O4@SiO2
Fe3O4 was prepared as the method reported in the previous literature [27]. Fe3O4@SiO2 nanospheres were prepared by a typical sol–gel method and detailed procedure list as follows [28]. Fe3O4 (0.1 g) nanospheres were dispersed in the mixture of ultrapure water (10 mL), ethanol (30 mL), and 1.2 mL of NH3·H2O. After the ultrasonication was continued for 1 h, 0.2 mL of TEOS was added to the above solution, and the reaction was maintained at 30 ℃ for 4 h. The obtained materials were washed three times with water and ethanol and dried at 60 ℃ under vacuum.
2.3 Preparation of Fe3O4@mTiO2
A uniform mesoporous TiO2 shell was coated onto Fe3O4@SiO2 according to the method reported previously [29, 30]. The previously prepared Fe3O4@SiO2 (0.2 g) nanoparticles and NH3·H2O (0.2 mL) were dispersed in ethanol (100 mL) with the aid of ultrasonication for 15 min. Then, 0.75 mL tetrabutyl titanate (TBOT) was added dropwise to the mixture subsequently, and the above system was maintained at 45 °C for 24 h. The obtained nanomaterials were isolated by magnet and washed with water and ethanol, dried under vacuum, and calcined in air at 500 °C for 2 h to form a mesoporous structure.
2.4 Preparation of RAFT agent modified Fe3O4@mTiO2 nanoparticles
Firstly, Fe3O4@mTiO2 (0.1 g) was dispersed in a solution containing azido-functionalized dopamine in CH2Cl2. After stirring for 24 h, the azido-functionalized Fe3O4@mTiO2 was obtained after washed with CH2Cl2 and dried under vacuum.
Forty milligram of alkynylated 2-dithiobenzoic acid butyrate (CPDB) and 80 mg of Fe3O4@mTiO2-N3 were dispersed in 25 mL of DMSO. After 15 min of sonication, 3.575 mg of CuSO4·5H2O and 14.2 mg of sodium ascorbate were separately dissolved in 1 mL water, which was added to the above solution subsequently. The mixture was mechanically stirred at 50 °C for 24 h. The solid product was isolated by magnet and washed several times with water and ethanol and dried under vacuum to obtain Fe3O4@mTiO2-CPDB. The synthesis of alkynylated CPDB and the corresponding 1H NMR spectra (Figure S5) are detailed in the supporting information.
2.5 Preparation of Fe3O4@mTiO2@MIP/NIP
4-VP and EGDMA are used as functional monomers and crosslinkers, respectively. Briefly, 0.21 mL of 4-VP and 136 mg of TBBPA were dissolved in 50 mL of anhydrous toluene and mechanically stirred under N2 for 10 h. Then, 50 mg of Fe3O4@mTiO2-CPDB was dispersed in the mixture by means of ultrasonic, followed by adding EGDMA (1.189 g) and AIBN (0.02 g), and the reaction was maintained at 60 °C for 24 h under N2 protection to obtain Fe3O4@mTiO2@MIP. TBBPA was removed using methanol-acetic acid (9:1, v: v) mixed eluent until no TBBPA could be detect by UV–vis spectrophotometer.
The non-imprinted polymer Fe3O4@mTiO2@NIP was prepared in same way without addition of the TBBPA.
2.6 Characterization
Fourier infrared spectrometer (FT-IR, VECTOR-22) was used to obtain the FT-IR spectra of the materials. The microscopic morphology of the sample was observed by transmission electron microscopy (TEM, JEM-2100). The structure of organic species was characterized using nuclear magnetic resonance spectrometer (ADVANCE III 400 MHz). The chemical state of some key element was characterized using an X-ray photoelectron spectroscopy (XPS, AXIS SUPRA). High-performance liquid chromatograph (HPLC-1525) was used to detect the content of TBBPA and its structural analogues in adsorption experiment. The sample injection volume was 10 μL. The mobile phase was composed by methanol and ultrapure water with the ratio of 75:25 (v: v) and the flow rate was 1.0 mL min−1. BPA, BIP, and BP were detected by ultraviolet detector at 278 nm, and TBBPA was detected at 292 nm.
2.7 Binding experiments
The binding ability of Fe3O4@mTiO2@MIP and Fe3O4@mTiO2@NIP for TBBPA was calculated by adsorption experiments. In static adsorption experiments, 10 mg of MIP/NIP nanoparticles was mixed with 10 mL of TBBPA solution in methanol–water (1:1, v: v) in a screw-capped glass tube and sealed and placed in a 30 °C constant temperature shaker for several hours. The concentration of TBBPA varies from 10 to 100 mg L−1. In the kinetic experiments, 10 mg of imprinted or non-imprinted polymer was added to TBBPA solution (10 mL) at a concentration of 10 mg L−1 and shaken for different intervals in a 30 °C constant temperature shaker. The MIP/NIP was isolated by magnet, and the resulting supernatant containing TBBPA was measured in HPLC. The adsorption amount of the adsorbent is calculated by the following equation [31,32,33]:
where Qe (mg g−1) is the equilibrium adsorption amount of TBBPA, V (mL) represents the total volume, Ct (mg L−1) represents the equilibrium concentration of TBBPA, Co (mg L−1) represents the initial concentration of TBBPA, and m (mg) is the mass of Fe3O4@mTiO2@MIP or Fe3O4@mTiO2@NIP.
2.8 Selectivity studies
BPA, BIP, and BP were selected as structural analogue to evaluate the selectivity of Fe3O4@mTiO2@MIP. 10 mg of Fe3O4@mTiO2@MIP and Fe3O4@mTiO2@NIP was dispersed in 10 mL of TBBPA and three structural analogues solution with the same concentration (18.5 μmol L−1) using methanol–water (1:1, v: v) as solvent, respectively. The mixture was shaken at 30 °C for 3 h, and the content of TBBPA and its analogues after adsorption was measured using HPLC.
For competitive experiments, TBBPA, BPA, BIP, and BP were dissolved together in a 10 mL of methanol–water mixed solvent (1:1, v: v), and to ensure the same concentration (18.5 μmol L−1) of each substance, 10 mg of Fe3O4@mTiO2@MIP was dispersed in the above solution and shaken at 30 °C for 3 h. The content of each component was also measured using HPLC.
3 Results and discussion
3.1 Preparation of the Fe3O4@mTiO2@MIP/NIP
The synthesis of MIP is illustrated as Scheme 1. Firstly, monodisperse Fe3O4 nanospheres were prepared by solvothermal method. SiO2 layer was then coated on the surface of Fe3O4 by hydrolysis of TEOS to prevent the leakage and corrosion of Fe3O4 nanoparticles. The outer mesoporous TiO2 layer was prepared by hydrolysis of TBOT, followed by annealing at 500 °C. Azido was then introduced via azido-functionalized dopamine based on a convenient non-covalent effect so that alkynyl-terminated CPDB could be introduced onto the mesoporous support by click chemistry. Finally, the MIP was grafted onto the surface of the support through RAFT polymerization with 4-VP and EGDMA as functional monomer and crosslinker, respectively.
The influence of molar ratio between 4-VP and EGDMA on the imprinting performance was investigated. In general, more functional monomer template complex will be formed as increasing the proportion of the functional monomer. But excessive functional monomer will also produce non-specific binding sites which are generated by the residues of non-assembled functional monomers. Meanwhile, the functional monomers were associated with each other when excessive functional monomers were added, which will decrease the binding sites. The proportion of crosslinker would affect the rigidity of the polymer skeleton and play an important role in the stabilization of the recognition sites. If the crosslinking degree of the as-prepared polymer was low owing to the insufficient dosage of crosslinker, the cavities of the obtained MIP would not be stable and consequently led to the poor binding capacity to target molecule. Figure S6 shows the binding efficiency toward TBBPA of the imprinted and non-imprinted polymers which was prepared with different molar ratio of 4-VP to EGDMA at 1:1, 1:3, and 1:5, respectively. The imprinted factor (IF) was calculated using the following formula [34]:
where QMIP and QNIP correspond to the binding amount of TBBPA by the imprinted and non-imprinted polymer, respectively. Correspondingly, the IF values were 1.71, 2.00, and 1.76. It is clearly seen that the imprinted polymer shows the best binding performance when the ratio of 4-VP to EGDMA is 1:3. Under this condition, the assembly between 4-VP and TBBPA becomes sufficient, and more discerning binding sites which are easily accessible can be obtained with the action of the crosslinker.
3.2 Characterization
Figure 1 shows the TEM morphology of the nanoparticles at each stage of the preparation procedure. Fe3O4 nanospheres prepared by solvothermal method exhibit a regular spherical structure of about 200 nm in diameter and exhibit good dispersibility (Fig. 1a, b, c). After SiO2 was coated on the surface of Fe3O4 by a typical sol–gel method, the as-prepared Fe3O4@SiO2 (Fig. 1d, e, f) exhibits smoother surface than Fe3O4. The spherical structure of Fe3O4 keeps well after SiO2 coated. The thickness of SiO2 layer is approximately 60 nm. After TiO2 layer was further coated, the thickness of shell was increased further, which can be clearly observed in Fig. 1g, h, and i. The obtained TiO2-coated magnetic nanoparticles are annealed at 500 °C to remove small molecules; a significant change in the roughness of the shell is observed as shown in Fig. 1j, k, and l. This demonstrates the formation of porous structure of TiO2 shell with thickness of about 22 nm. As shown in Fig. 1m, n, and o and Figure S7, a uniform thin shell layer appears at the surface of the TiO2 layer after the imprinted polymer was prepared by RAFT polymerization.
The functional groups of the materials that prepared in different stage are investigated by FT-IR, and the spectra are shown in Fig. 2. The absorption peaks at 450 and 570 cm−1 in Fig. 2a are ascribed to the vibration of the Fe–O, and the absorption band around 1390 cm−1 is caused by the presence of the carboxylate group, which is due to the addition of trisodium citrate in Fe3O4 preparation process [2]. After SiO2 was coated, the new characteristic peak at 1091 cm−1 in Fig. 2b indicates the stretching vibration of Si–O-Si. The adsorption band around 805 cm−1 is caused by Si–O vibration [35, 36]. Figure 2c is the FT-IR curve of Fe3O4@mTiO2. The characteristic absorption occurring in the 400–700 cm−1 belongs to the Ti–O-Ti and Ti–O stretching vibration modes [37], which indicated that the TiO2 layer was formed. After Fe3O4@mTiO2 was modified by azido-functionalized dopamine, the new peak around at 2100 cm−1 in Fig. 2d can be attributed to the stretching of N = N = N, and conform azido is successfully introduced to the surface of mesoporous support [38]. After click chemistry between azido and alkynyl, the characteristic peak appearing at 1166 cm−1 in Fig. 2e corresponds to -C = S, which indicates that the RAFT agent was successfully grafted to the surface of support [39]. In the spectrum of Fe3O4@mTiO2@MIP (Fig. 2f), the characteristic peak of C = C stretching from the pyridine ring was detected at 1457 cm−1, which suggested that the imprinted polymer layer was formed on the surface of Fe3O4@mTiO2 [40, 41]. The presence of EGDMA can be confirmed by the appearance of stretching vibration adsorption peaks at 1741 cm−1 and 1647 cm−1 [42, 43].
The crystal structure of the materials at each stage was further characterized by using XRD (Fig. 3). The characteristic diffraction peak in Fig. 3a at 2θ = 30.0°, 35.5°, 43.2°, 53.8°, 57.2°, and 62.6° is matched well with Fe3O4 nanoparticles [44,45,46]. The same XRD signal in Fig. 3b indicates that the coating of the SiO2 layer does not affect the crystal structure of magnetic core. Subsequently, after the TiO2 layer was coated and calcined at 500 °C, the new characteristic diffraction peaks in Fig. 3c were well-directed to the anatase TiO2, demonstrating that the emerge of the porous structure of TiO2 was attributed to the voids between self-aggregated nanocrystals [29, 47,48,49]. After MIP was prepared, the diffraction peaks of Fe3O4@mTiO2@MIP in Fig. 3d are similar to the peaks of Fe3O4@mTiO2 in Fig. 3c, indicating that the process of polymerization on the surface of TiO2 does not affect the crystal form of TiO2[50, 51].
Figure 4 illustrates the magnetic properties of the materials prepared at each stage. The curves a, b, c, and d are hysteresis curves of Fe3O4, Fe3O4@SiO2, Fe3O4@mTiO2, and Fe3O4@mTiO2@MIP, respectively. As the experiment progressed, the decrease of specific saturation magnetizations was caused by the encapsulation of SiO2, TiO2, and MIP layer. But the saturation magnetization of Fe3O4@mTiO2@MIP is still 23 emu/g, which ensure that it could be quickly and completely separated by the aid of a magnet. At the same time, it can be seen that all of the samples exhibit superparamagnetic behavior because the coercivity and remanence of the sample are not detected [17, 52]. Sensitive magnetic response is important for the later application of these samples.
The composition of the nanoparticles were further characterized by XPS. The signal located at 457 eV can be attributed to Ti 2p in the wide scan spectra of Fe3O4@mTiO2 (Fig. 5Aa) [53]. In Fig. 5Ab, the N 1 s peak appears at 398.5 eV in the wide scan spectra of Fe3O4@mTiO2-N3, suggesting that the azido was introduced on the surface of Fe3O4@mTiO2 by azido-functionalized dopamine successfully [54]. The S 2p peak at 164 eV in Fe3O4@mTiO2-CPDB indicating CPDB was successfully grafted onto the Fe3O4@mTiO2 (Fig. 5Ac) [55].
In the high-resolution spectrum of Ti in Fe3O4@mTiO2 (Fig. 5B), two peaks appeared at 458.3 eV and 464.1 eV can be attributed to Ti2p3/2 and Ti2p1/2, indicating that mesoporous TiO2 shell was successfully formed [53, 56,57,58]. In the high-resolution spectrum of the N element in Fe3O4@mTiO2-N3 (Fig. 5C), the singles at 398.6, 399.8, and 402.2 eV correspond to C-N, -N–H, and -N = , respectively [28, 59, 60]. It was proved that the azido functional dopamine was effectively grafted on the surface of TiO2. In the spectrum of S2p in Fe3O4@mTiO2-CPDB (Fig. 5D), the appearance of C = S (160.9 eV) and C-S-C (164.5 eV) peaks indicates that CPDB was successfully grafted onto the Fe3O4@mTiO2 by click chemistry [55]. By fitting the C 1 s spectra of Fe3O4@mTiO2@MIP curve (Fig. 5E), four peaks at the binding energy of 284.6, 286.0, 286.6, and 288.6 eV were caused by the presence of C = C/C–C/C-H, C-N/C = S, C = N/C-O/C-S, and C = O, respectively. The content of C = C/C–C/C-H, C-N/C = S, C = N/C-O/C-S, and C = O is 80.6%, 14.3%, 3.7%, and 1.4%, respectively [61]. In the high-resolution spectrum of the O element in Fe3O4@mTiO2@MIP in Fig. 5F, the peaks at 530 eV and 532.5 eV correspond to the O = C and O-C, respectively [62]. The overall analysis of the XPS spectrum fully confirmed that the imprinted polymer layer was well-formed on the surface of the Fe3O4@mTiO2 by RAFT polymerization.
The specific surface area and porosity of Fe3O4@mTiO2 were evaluated by N2 adsorption–desorption isotherms. As shown in Fig. 6a, the isotherms of Fe3O4@mTiO2 exhibit a typical type IV isotherm, and the specific surface area of the Fe3O4@mTiO2 obtained by Brunauer–Emmett–Teller analysis is 69.818 m2 g−1. At P/P0 = 0.05–0.35, a gentle increase in the amount of adsorption indicates that the N2 was adsorbed on the inner surface of the mesopores in a single layer to a plurality of layers. When P/P0 is between 0.40 and 0.80, the sudden increase in the amount of adsorption reflects the size of the sample pore size. At the higher relative pressure stage, the desorption isotherm does not coincide with the adsorption isotherm, and the desorption isotherm is above the adsorption isotherm, indicating an H3 hysteresis loop depending on the type of hysteresis loop [63]. This feature of the material will be better defined for the identification of the template and provides a higher binding capacity. Figure 6b shows the pore size distribution curve; the average pore diameter of the material obtained according to the Barrett-Joyner-Halenda pore size distribution curve was 4.626 nm, indicating the presence of mesopores structure in the matrix.
3.3 Absorption kinetics of Fe3O4@mTiO2@MIP
As shown in the adsorption kinetic curve in Fig. 7a, the adsorption capacities of Fe3O4@mTiO2@MIP and Fe3O4@mTiO2@NIP increased with time, and the adsorption capacity reached equilibrium after 20 min. Compared to the equilibrium time of TBBPA imprinted polymer that prepared by traditional free radical polymerization method [4], the equilibrium time in this work only takes 20 min, which is dramatically shorter than the reported valve of 40 min. This phenomenon is mainly thanks to the controllability of RAFT polymerization; the thin imprinted layer makes the imprinted sites more accessible to TBBPA and exhibits faster binding capabilities. It is clearly shown in Fig. 7a that the binding amount of Fe3O4@mTiO2@MIP is higher than that of Fe3O4@mTiO2@NIP due to the specific imprinted site generated on the surface for specific recognition of TBBPA.
The adsorption mechanism of the imprinted polymer was explained by using the following pseudo-first-order and pseudo-second-order kinetics models; the equations of them are depicted in following Eqs. (3–4), respectively [64, 65]:
wherein Qt and Qe represent the adsorption amount at t and equilibrium, t represents the adsorption time, and k1 and k2 represent the pseudo-first-order rate constant and the pseudo-second-order rate constant, respectively.
From the fitting curve of pseudo-second-order kinetic model in Fig. 7b and the relevant parameters that listed in the Table 1, it is suggested that the pseudo-second-order adsorption kinetics model agreed better with the adsorption process of TBBPA by MIP/NIP and the correlation coefficient of MIP was 0.999. At the same time, the experimental Qe, exp is closer to the theoretically calculated Qe, cal. This indicates that chemisorption controls the adsorption of TBBPA by Fe3O4@SiO2@mTiO2@MIP, and TBBPA binds to the identification site in the imprinted polymer layer by a non-covalent bond [66].
3.4 Adsorption isotherms of Fe3O4@mTiO2@MIP
The static adsorption experiment was also conducted to further understand the adsorption capability of Fe3O4@mTiO2@MIP and Fe3O4@mTiO2@NIP. As shown in the adsorption isotherms in Fig. 8a, the adsorption amount of Fe3O4@mTiO2@MIP and Fe3O4@mTiO2@NIP increases as the solution concentration of TBBPA increases and reaches a state of adsorption saturation after a certain time. However, the adsorption amount of Fe3O4@mTiO2@MIP was significantly greater than that of Fe3O4@mTiO2@NIP, indicating the higher specific binding ability of Fe3O4@mTiO2@MIP to the template molecule, since the imprinted sites existed on the material surface. The adsorption capacity of the imprinted polymer for TBBPA that prepared on the non-porous carrier was also studied. As can be seen from Fig. 8a, both the Fe3O4@TiO2@MIP and Fe3O4@TiO2@NIP exhibit weaker adsorption capacity towards TBBPA than Fe3O4@mTiO2@MIP/NIP, respectively. The Qmax of the imprinted polymer prepared (41.67 mg g−1) on the mesoporous support was 1.6 times higher than that prepared on non-porous support (25.64 mg g−1). The porous structure of the support can provide more binding site and make recognition sites more accessible for TBBPA [21]. The experiment results further confirmed that mesoporous structure of support exhibits more advantages than non-porous support as the imprinted polymer carrier.
The adsorption mechanism of Fe3O4@mTiO2@MIP/NIP was determined according to two different adsorption isotherms of Langmuir and Freundlich; the equations for the two models are as follows [64]:
Among them, Qm represents the maximum adsorption capacity of the imprinted material, Qe represents the adsorption capacity at the time of adsorption equilibrium, and Ce is the concentration of TBBPA at equilibrium. Kl is the adsorption equilibrium constant, and n and KF represent the adsorption strength and relative adsorption capacity, respectively.
The Langmuir isotherm adsorption model fitting curve in Fig. 8b and the data list in Table 2 clearly show that the adsorption process matches well with Langmuir isotherm equation, and the correlation coefficient of MIP is 0.995. The results indicate that the Langmuir isotherm equation is more appropriate for defining the adsorption of TBBPA. Therefore, it can be considered that TBBPA is adsorbed on the surface of the Fe3O4@mTiO2@MIP in the form of a monomolecular layer [67]. The Qm of Fe3O4@mTiO2@MIP for TBBPA was 41.67 mg g−1 and was higher than the value reported in literature [5, 68]. This is mainly due to the advantages generated by RAFT polymerization and mesoporous structure of the outer shell which can provide more binding sites to effectively improve the binding capacity [21].
3.5 Selectivity of Fe3O4@mTiO2@MIP nanoparticles
Excellent selectivity for TBBPA is crucial for the as-prepared Fe3O4@mTiO2@MIP. Therefore, some compounds (BPA, BIP, and BP) with similar structures to TBBPA were selected for comparative experiments. Their chemical structures are shown in the Fig. 9.
The same amount of Fe3O4@mTiO2@MIP and Fe3O4@mTiO2@NIP was separately dispersed in the solutions of TBBPA, BPA, BP, and BIP with the same concentrations, and the removal efficiency of imprinted and non-imprinted polymer for TBBPA and its structural analogues was examined. It is found from the results in Fig. 10 that the removal efficiency of Fe3O4@mTiO2@MIP for TBBPA is significantly higher than that of the other three substances, which proves the specific recognition property of the imprinted material for TBBPA. This is mainly caused by the specific recognition cavity exist at the surface of Fe3O4@mTiO2@MIP, which is completely corresponding to the shape, size, and spatial organization of TBBPA, while BIP, BP, and BPA are not complementary to the recognition site, and the removal efficiency is lower. The above results further demonstrate that Fe3O4@mTiO2@MIP can be used to selectively detect TBBPA.
In addition, competitive binding experiments were implemented to verify the specific binding property of Fe3O4@mTiO2@MIP to TBPPA. A mixed solution (10 mL) with the equimolar concentrations (18.5 μmol L−1) of TBBPA, BPA, BIP, and BP was prepared, and then 10 mg of Fe3O4@mTiO2@MIP was added. As shown in Figure S8, the Fe3O4@mTiO2@MIP presents the highest removal efficiency for TBBPA. Conversely, the removal efficiency for the other three substances was very low. This indicates that the imprinted polymer is capable of specifically recognizing TBBPA in a complex environment.
3.6 Reusability of Fe3O4@mTiO2@MIP
Reusability is critical for the practical application of imprinted materials. The recyclability of the imprinted material was detected by performing adsorption–desorption-resorption of the imprinted material. Figure 11 shows the adsorption effect of the imprinted material on TBBPA during 5 cycles. It was observed that it still maintains a high adsorption amount without significant decrease and indicates the imprinted material has excellent stability.
4 Conclusions
Magnetic surface molecularly imprinted polymer was prepared using magnetic mesoporous Fe3O4@mTiO2 nanoparticles as support by RAFT polymerization and was used for rapid detection of TBBPA. The prepared imprinted material has excellent specific binding properties for TBBPA in short time. In addition, the presence of the magnetic core facilitates the rapid separation of the imprinted material. The combination of RAFT polymerization and mesoporous structure of outer TiO2 layer makes more effective recognition site existence which can affect specific binding properties of obtained imprinted polymer effectively. In practical applications, satisfactory selection performance and recyclable results indicate a promising separation of TBBPA in complex environments.
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Funding
The authors would like to express their gratitude for research funding provided by the National Natural Science Foundation of China (Program No. 21806097, 21978164, 22078189), the Industrialization Project of Shaanxi Education Department (Program No. 19JC010), the Scientific Research Program Funded by Shaanxi Provincial Education Department (Program No. 18JK0104), and the Research Starting Foundation of Shaanxi University of Science and Technology (Program No. 2016BJ-80).
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Shao, Y., Bai, H., Wang, H. et al. Magnetically sensitive and high template affinity surface imprinted polymer prepared using porous TiO2-coated magnetite-silica nanoparticles for efficient removal of tetrabromobisphenol A from polluted water. Adv Compos Hybrid Mater 5, 130–143 (2022). https://doi.org/10.1007/s42114-021-00361-7
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DOI: https://doi.org/10.1007/s42114-021-00361-7