Skip to main content
ACS AuthorChoice logoLink to ACS AuthorChoice
. 2025 Apr 30;17(19):28568–28584. doi: 10.1021/acsami.5c03038

Insights into the Imprinting and Rebinding Performance of Molecularly Imprinted Hybrids for Bisphenol A and Bisphenol F

Kae-Zheng Chin †,, Sue-min Chang †,*
PMCID: PMC12086839  PMID: 40304560

Abstract

graphic file with name am5c03038_0014.jpg

This study investigates the factors influencing the imprinting performance of molecularly imprinted hybrids (MIHs) with various template/monomer associations and their corresponding adsorption ability for three bisphenol analogues, bisphenol A (BPA), 2,2′-bisphenol F (2BPF), and 4,4′-bisphenol F (4BPF). Styrene (St) and methacrylic acid (MAA) were selected as the primary functional monomers for template complexation. Compared with hydrophilic MAA monomers, hydrophobic St monomers were more favorable for BPA imprinting, despite the lower binding energy of π–π interactions compared to hydrogen bonds. However, St monomers were unsuitable for 4BPF imprinting, while 2BPF exhibited limited complexation with MAA monomers. Among the bisphenols, BPA demonstrated the strongest imprinting capability, leading MIHs to exhibit the highest imprinting factor (IF = 14–18), adsorption capacity (Qmax = 43.7–47.6 mg/g), binding affinity (KL = 4.52–6.74 L/mg, ΔH°ads = −35.2 to −38.9 kJ/mol, and ΔS°ads = −40.5 to −50.6 J mol–1 K–1), and selectivity over 2BPF and 4BPF (2.0–3.5). In contrast, 2BPF- and 4BPF-imprinted hybrids exhibited significantly lower adsorption capacities (Qmax = 19.4–26.7 mg/g) and binding affinities (KL = 1.22–4.35 L/mg) for their respective templates. In competitive adsorption systems, bisphenol rebinding followed the trend BPA > 2BPF > 4BPF, regardless of which template was used for imprinting. Based on NMR analysis, the superior structure-directing and competitive rebinding abilities of BPA are attributed to the restricted rotation of its two phenyl groups, p-OH groups, and additional -CH3 groups on the bridged carbon, which enhance π–π stacking, H-bond, CH−π, and hydrophobic interactions within the imprinted cavities. In contrast, the o-OH groups of 2BPF and the rotational phenyl groups of 4BPF hinder their imprinting and rebinding via H-bond and π–π interactions, respectively.

Keywords: molecular imprinting, bisphenol adsorption, NOESY NMR analyses, noncovalent forces, binding interaction

1. Introduction

Bisphenol A (BPA) and its substitute, bisphenol F (BPF), widely found in various consumer products, are known for their adverse effects as endocrine-disrupting chemicals.13 To address their impact on human health and the environment, there is an increasing demand for advanced adsorbents to effectively separate and concentrate these compounds in water. Molecular imprinting is a promising approach to create artificial recognition materials exhibiting high binding affinity and selectivity for analytes of interest.47 This method involves binding template molecules with functional monomers, cross-linking the template/monomer complexes to form a three-dimensional polymeric matrix, and subsequently removing the incorporated template from the resulting polymers. Understanding of the molecular interactions within self-assembled imprinting systems is crucial for designing adsorbents with the desired adsorption performance. While molecular imprinting has been extensively employed to develop adsorbents for various applications, fundamental research on the factors governing imprinting effectiveness and resulting adsorption ability and selectivity among structural analogues remains limited, leaving some issues unresolved.

Effective imprinting relies on stable template/monomer complexes.8 Due to simplicity and reversibility, noncovalent bonds are generally employed to complex templates with functional monomers. Monomers containing -COOH, -CONH2, pyridine, or aromatic functional groups, such as methacrylic acid (MAA),9,10 acrylamide (AAM),11 4-vinylpyridine (4-VP),12 and styrene (St),13 are commonly selected to establish H-bonds or π–π interactions with bisphenols. The binding energies of these functional monomers to BPA are calculated to be 10.16–13.61 kcal/mol for H-bonds, while the π–π stacking energy associated with St is 0.7–3.0 kcal/mol.1416 Compared to π–π interactions, stronger H-bonds are considered more advantageous for imprinting efficiency. However, this benefit may be offset by the formation of H-bonded dimers between monomers, which can hinder their interaction with templates.17 Additionally, template rebinding via H-bonds may be interfered in aqueous environments.5 In contrast, the hydrophobicity of St moieties in polymers facilitates the partitioning of bisphenols into the imprinted matrix.18 Furthermore, despite the lower binding energies of π–π interactions, St monomers have demonstrated high imprinting performance and strong adsorption selectivity for BPA.19 To date, the contributions of H-bonds and π–π interactions to the imprinting of bisphenols have not yet been systematically compared and evaluated. Moreover, binding energies and imprinting performance vary among bisphenol analogues for a given functional monomer.20,21 Since both H-bonds and π–π interactions are orientation-dependent, the variation is associated with template molecular configurations. However, the limitation of these two binding mechanisms in imprinting, as well as the structural directing ability of bisphenol analogues concerning the analogue molecular configurations, has not yet been clarified.

Although imprinted cavities exhibit strong exclusion ability for compounds with sizes and shapes differing from the templates, the customized binding sites can also accommodate structural analogues to a certain extent.22 Based on this characteristic, dummy-template molecularly imprinted polymers (DMIPs) have been developed using compounds with similar structural features and chemical attributes to the target analytes as alternative templates to avoid positive bias caused by the release of template residues when the DMIPs are used to enrich analytes for trace-level analysis.23 DMIPs have demonstrated their ability to recognize target molecules as effectively as conventional imprinted polymers. In some cases, they even exhibit greater specificity for the target compared to the dummy template, in particular, as observed in the adsorption of BPA by DMIPs prepared using tetrabromobisphenol A (TBBPA) or 4,4′-bisphenol F (4BPF) as dummy templates.2428 The mechanisms underlying this distinct selectivity for the target analytes over the dummy templates remain unclear.

In this study, we aimed to investigate the factors influencing the imprinting and rebinding of three bisphenols, BPA, 2,2′-bisphenol F (2BPF), and 4BPF, in an organic–inorganic hybrid system with a focus on template molecular configurations, hydrophilicity/hydrophobicity of functional monomers, and compatible intermolecular interactions between the template and monomers/polymers through π–π interactions or H-bonds. Previously, we developed a molecularly imprinted hybrid (MIH) targeting BPA by cross-linking styrene (St)/methyl methacrylate (MMA) copolymers with SiO2 clusters.7 The MIH exhibited an impressive BPA adsorption capacity (40.3 mg/g), a substantial imprinting factor (14), and remarkable selectivity. In this study, the MIH was used as a model system to further explore imprinting characteristics and guest–host interactions with different structural analogues and functional monomers. The three bisphenol analogues, BPA, 2BPF, and 4BPF, as illustrated in Figure 1, were used as templates. Two primary functional monomers, St and MAA, were employed to interact with the templates through π–π interactions and H-bonds, respectively, while MMA monomers were used to form linear copolymer chains that encapsulated the template and shaped imprinted cavities along the template conformation. The adsorption ability, thermodynamic parameters, and selectivity of the MIHs/non-imprinted hybrids (NIHs) were systematically analyzed. Moreover, one- and two-dimensional 1H nuclear magnetic resonance (NMR) spectroscopy was utilized to determine the interactions between the monomers/copolymers and the templates at molecular levels. By cross-comparing the adsorption and NMR results, optimal template/monomer combinations for achieving high adsorption capacities were identified. The key molecular features of the templates and functional monomers that determined their superiority or limitations in imprinting and adsorption were clarified. Moreover, guidelines for selecting suitable functional monomers based on the molecular configuration of templates to achieve the desired adsorption performance were established.

Figure 1.

Figure 1

Chemical structures of templates (a) BPA, (b) 2BPF, and (c) 4BPF and monomers (d) St, (e) MAA, and (f) MMA used in this study.

2. Experimental Section

2.1. Preparation of Molecularly Imprinted Hybrids

The synthesis of MIHs followed the procedures outlined in our previous study7 and is illustrated in Scheme 1. BPA (99%, Tokyo Chemical Industry Co., Ltd.), 2BPF (98%, Sigma-Aldrich), and 4BPF (98%, Alfa Aesar) were employed as templates. St (>99%, Sigma-Aldrich) and MAA (99%, Thermo) were used as primary functional monomers to form complexes with templates, while MMA (99%, Alfa Aesar) was used to form linear polymeric chains. A silane coupling agent, 3-(methacryloxyl) propyltrimethoxysilane (MPS, 97%, Alfa Aesar), was used to covalently bond polymer chains and SiO2, and tetraethyl orthosilicate (TEOS, 98%, Seedchem) was used as the precursor of the inorganic cross-linker, SiO2. The compositions of the templates and monomers for different samples are listed in Table 1. The template and functional monomer at desired amounts were dissolved in 6.0 mL of anhydrous ethanol (99.5%, ECHO) under agitation for 20 min, followed by the addition of MMA and MPS (5 mmol). Polymerization was initiated by adding 1.0 mL of a potassium persulfate (KPS, 99%, Sigma-Aldrich) aqueous solution at 70 °C, with the concentration of the KPS solution adjusted to ensure that the added KPS amount was 1.0 mol % of the total monomers. Polymerization proceeded at 70 °C for 6 h. Subsequently, TEOS (15 mmol), 0.9 mL of DI water, and 1.0 mL of a 1.0 M HCl solution were added to the solution to cross-link the polymer chains by forming SiO2 clusters via sol–gel reactions. After 2 h reactions, the colloidal solution was transferred into a crucible and dried at 50 °C overnight, and the obtained solid products were ground into fine powders. The templates were then extracted from the MIH powders with methanol using a microwave extraction method. The extraction was conducted at 75 °C for 20 min and repeated 10 times to ensure complete removal of the template. For comparison, non-imprinted hybrids (NIHs) were also prepared using identical recipes and procedures as described above but without the addition of templates. The morphologies, textures, and particle sizes of MIHs and NIHs were characterized by scanning electron microscopy (SEM), transmission electron microscopy (TEM), N2 adsorption–desorption, and dynamic light scattering (DLS), as detailed in the Supporting Information. Additionally, the minimal release of BPA from a St-based MIH after extraction to a methanol/acetic acid (9:1 (v/v)) eluent was analyzed using high-performance liquid chromatography-tandem mass spectrometry (HPLC-MS/MS) to ensure a negligible amount of the template remained in the MIH.

Scheme 1. (a) Schematic Diagram of the Preparation Procedures for MIHs and the Resulting Imprinting Structure and (b) Cross-Linking of Long Polymer Chains with SiO2 Clusters during the Synthesis of NIHs.

Scheme 1

In the absence of template hindrance, longer polymer chains are formed, resulting in larger particle sizes compared to MIHs. Additionally, stronger interactions among the extended polymer chains drive more SiO2 clusters to deposit on the particle exterior, leading to a denser structure in NIHs, in contrast to the looser, nanoporous structure in MIHs.

Table 1. Chemical Compositions for the Different Types of MIHs.

  template (mmol) primary functional monomer (mmol)
secondary functional monomer (mmol) silane coupling agent (mmol) inorganic cross-linker (mmol)
MIH BPA/2BPF/4BPF St MAA MMA MPS TEOS
St-based 1 2 a 5 5 15
MAA-based 1 a 2 5 5 15
MMA-based 1 a a 7 5 15
a

Not involved.

2.2. Adsorptions of Bisphenols

The binding affinity of MIHs for their templates was evaluated by conducting adsorption isotherms at 298, 308, 318, and 328 K. Each MIH (15 mg) was separately dispersed in 15 mL of a single-analyte aqueous solution (BPA, 2BPF, or 4BPF) at varying initial concentrations (10–100 mg/L). The suspensions were magnetically stirred for 2 h of adsorption, after which the adsorbents were removed by centrifugation. The concentration of unbound analytes in supernatants was determined using a UV–vis spectrometer (Hitachi 3010) based on the absorbance at 276, 272, and 275 nm for BPA, 2BPF, and 4BPF, respectively. The equilibrium adsorption amounts (Qe, mg/g) for the analytes were calculated using eq 1.

2.2. 1

where C0 (mg/L) is the initial concentration of analytes, Ce (mg/L) is the equilibrium concentration of unbound analytes, V (mL) is the volume of the solution, and m (mg) is the weight of MIHs or NIHs. The imprinting factor (IF) is defined as the ratio between the Qe of a MIH and its corresponding NIH (eq 2).

2.2. 2

The isotherms obtained at different temperatures were fitted with the Langmuir model to determine the Langmuir constant (KL). Thermodynamic parameters, including ΔG°ads, ΔH°ads, and ΔS°ads, were further derived based on the KL values.

2.3. Selective Adsorptions

The molecular recognition ability of MIHs and NIHs was assessed through competitive adsorption in aqueous solutions containing BPA, 2BPF, and 4BPF, with each bisphenol at an initial concentration of 20 mg/L. Equal amounts (20 mg) of MIHs or NIHs were separately suspended in 20 mL of the mixture under agitation. Following a 2 h adsorption period, the remaining concentrations of the bisphenols in the supernatants were analyzed using an HPLC instrument equipped with a photodiode array detector (HPLC-PDA, Waters 2695/2996). For HPLC analysis, 20 μL of supernatants was injected into the chromatography system, and the bisphenol analytes were separated using a hypersil BDS C18 column (Thermo, 4.6 mm × 250 mm, 5 μm particle size) with a mobile phase consisting of water/acetonitrile (50:50, v/v) at a flow rate of 1 mL/min. The absorbances of BPA and 4BPF were measured at 277 nm, while that of 2BPF was measured at 273 nm. The retention times of 4BPF, BPA, and 2BPF were 4.4, 5.7, and 6.7 min, respectively. The selective binding of MIHs for the analogues is determined by the relative selectivity coefficient (k′), as shown in eq 3, where k′ is derived from the selectivity coefficient (k, eq 4) and the distribution coefficient (Kd, eq 5).29

2.3. 3
2.3. 4
2.3. 5

where Qe (mg/g) represents the adsorbed amount of the target analyte or analogue and Ce (mg/L) denotes the remaining concentration in the supernatant at equilibrium.

2.4. Studies of Complex Formation by 1H NMR Spectroscopy

The interactions between the templates and functional monomers were examined using a 600 MHz NMR spectrometer (VARIAN VNMRS-600). One-dimensional 1H NMR analysis and two-dimensional 1H–1H nuclear Overhauser effect spectroscopy (NOESY) were conducted to explore the intermolecular interactions between bisphenols and functional monomers. For the experiments, 1.0 mmol of each template (BPA, 2PBF, or 4BPF) was separately mixed with 2.0 mmol of a functional monomer (St, MAA, or MMA) in dry DMSO-d6 according to the stoichiometry used for the preparation of MIHs. Additionally, to investigate the intermolecular interaction between the bisphenols and copolymers, including p(St-co-MMA), p(MAA-co-MMA), and pMMA, 2.0 mg of each template was individually mixed with 15 mg of the polymers in CDCl3 or DMSO-d6. These samples were analyzed by two-dimensional NOESY and 1H selective rotating-frame Overhauser effect spectroscopy (one-dimensional ROESY). p(St-co-MMA) and p(MAA-co-MMA) were synthesized with 2.0 mmol of St and 2.0 mmol of MMA and with 10 mmol of MMA and 10.0 mmol of MMA, respectively, while pMMA was synthesized with 10 mmol of MMA. Each synthesis was conducted by dissolving the monomers in 6.0 mL of anhydrous ethanol under stirring. Similar to the preparation for the MIHs, polymerization was initiated by adding 1.0 mL of a KPS aqueous solution (1.0 mol % of the total monomers) at 70 °C and continued for 6 h. The resulting polymers were precipitated by using methanol and separated from the suspensions by centrifugation. Subsequently, the obtained polymers were washed three times with methanol and then dried at 50 °C overnight.

3. Results and Discussion

3.1. Characteristics of MIHs and NIHs

MIHs and NIHs were prepared through radical-induced polymerization and sol–gel reactions, as described in our previous work.7 Initially, linear polymer chains were formed through the polymerization between functional monomers and a coupling agent, while the monomers had formed complexes with templates. Subsequently, sol–gel reactions between the coupling agent and a Si-based precursor cross-linked the polymer chains, resulting in 3D imprinted nanostructures (Scheme 1). In our earlier work, the material properties, including the morphology, texture, particle size, composition, and surface charge, of a St-based MIH imprinted with BPA molecules and its corresponding NIH were thoroughly characterized.7 The roles of the organic framework and inorganic cross-linker in imprinting and adsorption ability were also identified. The MIH and NIH were found to contain 37–40 wt % organic components and 60–63 wt % SiO2 moieties. The organic polymer was primarily responsible for analyte binding, while the rigid SiO2 moiety confined the conformation of the imprinted cavities, minimized nonspecific adsorption, and improved water compatibility, which synergistically contributed to a high IF (14) and a high selectivity of the MIH. Successful removal of the imprinted molecules from the MIH via methanol extraction was confirmed by the disappearance of the characteristic template peak at 1515 cm–1 in FTIR spectra. In this study, this fact was further verified by a reduction in particle aggregation and a decrease in particle size after the extraction, as observed through SEM and DLS characterizations (Figure 2a and Figure S1a,b). Additionally, LC-MS/MS analysis of methanol eluents confirmed minimal BPA release from the extracted MIHs (0.1 ng/mL) (Supporting Information).

Figure 2.

Figure 2

SEM images of St-based MIHs with the (a) BPA, (b) 2BPF, and (c) 4BPF imprints and (d) St-based NIH. (e) N2 adsorption–desorption isotherm curves of St-based MIHs and St-based NIH (inset). The filled symbol represents N2 adsorption, and the empty symbol represents N2 desorption. (f) Particle size distribution of each type of MIH and NIH in methanol. TEM images of (g) St-based MIH with BPA imprints and (h) St-based NIH. The inset in Figure 2h shows a higher magnification of a St-based NIH particle.

The morphologies, textures, and particle sizes of St-based, MAA-based, and MMA-based MIHs and NIHs were characterized by SEM, TEM, N2 adsorption–desorption, and DLS. Aggregates were observed in all MIHs and NIHs. For St-based MIHs, unclear grain boundaries were found in the BPA-imprinted hybrid due to stronger aggregation, whereas more distinct boundaries were noted in 2BPF- and 4BPF-imprinted hybrids (Figure 2a–c). Similarly, significant aggregation was observed in MAA- and MMA-based MIHs with BPA imprints (Figure S1c,d). In contrast to the MIHs, larger grain sizes were observed in the corresponding NIH powders (Figure 2d). Moreover, like BPA-imprinted hybrids, significant aggregation was noted in the NIH powders. The morphological features corresponded with the textural results. All of the MIHs and NIHs exhibited type II adsorption isotherms with H3 hysteresis loops (Figure 2e and Figure S2a–c), indicating slit-like pores. The pores, with a diameter of 3.6–4.1 nm, are attributed to voids between particles in the aggregates (Figure S2d–g). Due to significant aggregation, MIHs with BPA imprints showed small specific surface areas (SSAs) of 10.1–16.6 m2/g and small pore volumes of 0.011–0.033 cm3/g. In contrast, the 2BPF- and 4BPF-imprinted hybrids exhibited larger SSAs (27.8–99.0 m2/g) with larger pore volumes (0.026–0.085 cm3/g) (Table S1). In the absence of templates during the polymerization and cross-linking processes, the NIHs showed small SSAs (9.9–28.7 m2/g) as a result of large grain sizes and significant aggregation.

Suspended particle sizes of MIHs and NIHs were determined in methanol. The sizes of St-based, MAA-based, and MMA-based MIHs were 122–142, 122–164, and 190–255 nm, respectively. The particle sizes of NIHs, regardless of the types of functional monomers, were 255 nm (Figure 2f). These measurements were further confirmed by TEM analysis (Figure 2g,h). St-based MIH with BPA imprints and its corresponding NIH particles exhibited sizes of ca. 120 and 250 nm, respectively, which were close to those measured by DLS. The smaller particle sizes in the MIHs, compared to the NIHs, are attributed to hindered polymerization caused by the complexation of monomers with templates, resulting in shorter chains.30 The steric hindrance imposed by templates also led to a looser, nanoporous structure of St-based MIH particles, while St-based NIH particles were denser (Scheme 1). Based on the dependence of particle sizes on monomer–template interactions, the smaller particle sizes of St-based and MAA-based MIHs relative to those of MMA-based MIH suggest that the interactions between bisphenols and either St or MAA were stronger than those involving MMA. Particle aggregation of both MIHs and NIHs particles under dry conditions primarily arose from electrostatic attraction between SiO2 moieties on the surface. Since SiO2 clusters were formed through sol–gel reactions in the second stage to cross-link the preformed polymers during the preparation, a larger portion of SiO2 moieties was driven to be located in the outer region of hybrid particles.7 The uneven SiO2 distribution was more pronounced in the NIHs due to stronger interactions between the longer polymer chains formed in the absence of template-induced hindrance (Scheme 1b). Likewise, the more significant aggregation of BPA-imprinted hybrids, compared to 2BPF- and 4BPF-imprinted particles, suggests that the monomers/polymers interacted more strongly with BPA molecules than with the other two analogues. This hypothesis was further supported by subsequent adsorption results.

3.2. Adsorptions of MIHs Prepared with Different Template/Functional Monomer Associations

The adsorption ability of MIHs prepared with different template/monomer associations and their corresponding NIHs was examined to evaluate their imprinting performance. For comparison, MIHs and NIH containing only MMA moieties were also prepared, and their adsorption abilities were measured. Figure 3a–c illustrates the adsorption ability of St-, MAA-, and MMA-based MIHs and NIHs for their respective templates at a constant concentration of 20 mg/L. Regardless of the functional monomers, MIHs exhibited similar adsorptions for their corresponding templates. BPA adsorptions (12.01–13.27 mg/g) were the highest, followed by 2BPF (4.88–7.06 mg/g) and 4BPF adsorptions (4.63–5.35 mg/g). In contrast to the high adsorptions by MIHs, NIHs exhibited low adsorptions for all three bisphenols (0.51–2.47 mg/g), confirming the imprinting effect. The imprinting factors (IFs) are calculated as the ratio of adsorption amounts (Qe) by MIHs to those of the corresponding NIHs at equilibrium (eq 2). Instead of adsorption capacity (Qmax), Qe values are used for IF calculation as they comprehensively account for imprinting efficiency and effectiveness (eq S1). Compared to 2BPF and 4BPF, -BPA template resulted in the highest IF values (14–18) in both the St- and MAA-based systems. While 4BPF imprinting had the lowest IF (5.4) in the St-based system, 2BPF imprinting led to the lowest IF (5.3) in the MAA-based system. Compared to the St- and MAA-based systems, the absence of primary functional monomers decreased the IF values (2.3–5.0) for all three bisphenol templates in the MMA-based system. Nevertheless, BPA imprinting still exhibited the highest IF value (5.0), while the lowest IF value was found with 2BPF (2.3).

Figure 3.

Figure 3

Adsorption ability and IFs of different imprints in (a) St-based, (b) MAA-based, and (c) MMA-based systems. Adsorption isotherms of (d) St-based, (e) MAA-based, and (f) MMA-based MIHs for their respective bisphenol templates and (g) St-based, (h) MAA-based, and (i) MMA-based NIHs for the three bisphenols at 298 K. Qe and Ce are the adsorption amounts and concentrations of bisphenols at equilibrium, respectively.

Adsorption isotherms of MIHs for their corresponding bisphenol templates by at 298 K were further examined (Figure 3d–f) and fitted with the Langmuir (eq 6) and Freundlich models (eq 7) to determine the adsorption capacity and affinity.31

3.2. 6
3.2. 7

where Ce (mg/L) is the bisphenol equilibrium concentration, Qmax (mg/g) is the calculated maximum adsorption capacity, KL (L/mg) is the Langmuir binding affinity constant, and KF and n are the Freundlich constants and adsorption favorability, respectively. Regardless of the functional monomers used, the BPA-imprinted MIHs demonstrated the highest adsorption capacity for BPA. Table 2 lists the adsorption capacity and parameters derived from the two model fittings. The isotherm parameters obtained from the St-based and MAA-based MIHs exhibited strong correlations with the Langmuir model (R2 > 0.961), while the adsorption isotherms of MMA-based MIHs were closer to the Freundlich model (R2 > 0.971). This finding, coupled with the higher IF values in the St- and MAA-based systems than in the MMA-based system, indicates that the St and MAA monomers enhance imprinting quality, thereby promoting specific interactions with these bisphenols. While the adsorptions of BPA by both the St- and MAA-based MIHs were better fitted with the Langmuir model, the adsorptions of 4BPF and 2BPF in the St-based and MAA-based systems, respectively, were slightly closer to those of the Freundlich model. This result correlated with the high IF values of BPA imprints (14–18) and relatively low IF values of the 4BPF imprints (5.4) and 2BPF imprints (5.3) in the St-based and MAA-based systems, respectively, suggesting superior structural directing ability of BPA with functional monomers to create the high quality of imprinted sites. On the other hand, π–π interactions of 4BPF molecules with St monomers and H-bond interactions of 2BPF molecules with MAA monomers are unfavorable.

Table 2. Isotherm Parameters of Different Functional Monomer-Based MIHs for Their Respective Bisphenol Templates.

    Langmuir
Freundlich
MIH template Qmax (mg/g) KL (×10–2 L/mg) R2 n Kf R2
St-based BPA 44.8 6.74 0.994 1.94 4.83 0.977
2BPF 20.4 4.35 0.998 1.97 1.87 0.978
4BPF 26.7 1.22 0.962 1.33 0.52 0.981
MAA-based BPA 43.7 4.61 0.998 1.77 3.43 0.981
2BPF 24.9 2.14 0.961 1.60 1.08 0.990
4BPF 19.6 2.34 0.984 1.91 0.59 0.939
MMA-based BPA 47.6 4.52 0.986 1.79 3.81 0.994
2BPF 19.6 2.02 0.872 1.71 0.95 0.971
4BPF 21.0 2.69 0.933 1.82 1.34 0.974

Benefiting from effective imprinting with BPA templates, the BPA-imprinted hybrids exhibited the highest adsorption capacity (Qmax = 43.7–47.6 mg/g) and binding affinity (KL = 4.52–6.74 L/mg) toward BPA compared to the 2BPF- and 4BPF-imprinted hybrids for their respective templates (Qmax = 19.6–26.7 mg/g, and KL = 1.22–4.35 L/mg). The variations in adsorption capacities among different templates, yet similar adsorption capacities of a given compound across different functional monomer-based systems, reveal that the template conformation, rather than the type of functional monomer, primarily determines the imprinting efficiency. Although functional monomers have a weaker influence on imprinting efficiency, they significantly affect adsorption affinity. The highest affinity of BPA imprints for BPA molecules was observed in hybrids with St moieties (KL = 6.74 L/mg), compared to those with MAA (KL = 4.61 L/mg) and MMA moieties (KL = 4.52 L/mg). Since H-bonds are stronger than π–π interactions,1416 the advantage of St functional monomers in imprinting and rebinding is attributed to their hydrophobicity, which reduces solvent (ethanol or water) interference in template/monomer complexation and guest–host interactions. A similar trend was observed in 2BPF adsorption, but an opposite relationship occurred in 4BPF adsorption. While the lowest affinity of the 2BPF imprints was found in the MAA- and MMA-based systems (KL = 2.07–2.14 L/mg), the weakest interaction between the 4BPF imprints and their template occurred in the St-based system (KL = 1.22 L/mg). These results again correlate with the IF values, further supporting the unfavorable complexation between St monomers and 4BPF molecules. Additionally, H-bond formation with MAA moieties is more challenging for 2BPF, which has two o-OH groups. In contrast to the MIHs, NIHs in general exhibited low and nonspecific adsorptions (Figure 3g–i and Table S2).

3.3. Thermodynamic Parameters

To further evaluate the effectiveness of imprinting from an energy perspective, we focused on St- and MAA-based systems to measure adsorption isotherms at different temperatures ranging from 298 to 328 K, as depicted in Figure 4. The adsorption capacities of the three bisphenols by both St- and MAA-based MIHs decreased with an increase in temperature (Figure 4a–f). In contrast, the adsorption ability of the corresponding NIHs increased with temperature (Figure 4g–l). Since NIHs lack customized binding sites, adsorption primarily occurred at external surfaces due to the weak driving force for bisphenol migration through the matrix. However, an increased thermal energy can facilitate molecular diffusion into the interior by overcoming internal resistance.32,33 Additionally, it weakens polymer chain interactions to promote bisphenol solubilization within the organic matrix, thus increasing the level of adsorption. Among the three bisphenols, 4BPF exhibited the lowest adsorption by NIHs, likely due to the rotational flexibility of its phenyl groups, which may hinder diffusion through the dense network. Despite the increase in adsorption with temperature, the isotherms of NIHs were poorly fitted by the Langmuir model (Tables S2–S4), supporting the idea that the adsorption is primarily governed by nonspecific hydrophobic interactions between bisphenol molecules and the organic components of the NIHs. In contrast, the customized binding sites in MIHs, confined by SiO2 moieties, still maintained Langmuir-type adsorption behavior, although their adsorption efficiency decreased at higher temperatures.

Figure 4.

Figure 4

Adsorption isotherms of St-based MIHs with (a) BPA, (b) 2BPF, and (c) 4BPF imprints and those of MAA-based MIHs with (d) BPA, (e) 2BPF, and (f) 4BPF imprints for their respective templates at 298–328 K. Due to the similarity in the adsorption isotherms of 2BPF- and 4BPF-imprinted hybrids at 298 and 308 K, 328 K was selected to replace 308 K in these two systems to produce distinct adsorption results. Adsorption isotherms of St-based NIHs for (g) BPA, (h) 2BPF, and (i) 4BPF and MAA-based NIHs for (j) BPA, (k) 2BPF, and (l) 4BPF at 298–318 K. Qe and Ce are the adsorption amounts and concentrations of bisphenols at equilibrium, respectively.

The Langmuir constants of MIHs at various temperatures (KL–T) were obtained from the Langmuir model fitting. Thermodynamic parameters, including ΔG°ads, ΔH°ads, and ΔS°ads, were then calculated based on the Langmuir constants using the van’t Hoff equation (eq 8) and Gibbs free energy of adsorption (eq 9),34 as listed in Table 3.

3.3. 8
3.3. 9

where KL–T (L/mol) is the Langmuir constant derived from various temperatures, R is the universal gas constant (8.314 J K–1 mol–1), and T (K) is the adsorption temperature. Negative ΔG°ads values were obtained from all of the systems, indicating spontaneous adsorptions by the MIHs. Unlike 2BPF and 4BPF imprints, BPA imprints showed exclusively thermodynamically favorable adsorption in both St- and MAA-based systems for their template molecules. The highly negative ΔH°ads values (−35.2 to −38.9 kJ/mol) for BPA adsorption indicate stable BPA/imprint complexes. Furthermore, the highly negative ΔS°ads values (−40.5 to −50.6 J mol–1 K–1), as a result of the loss of randomness degree upon BPA adsorption, suggest intimate guest–host matching within the imprinted sites. Entropy not only relates to the ability of molecules to move, rotate, and vibrate within a confined space but also correlates with the extent of molecular substitution during adsorption.3537 Compared to BPA imprints in MAA-based MIH (ΔS°ads = −40.5 J mol–1 K–1), the more negative ΔS°ads value (−50.6 J mol–1 K–1) was observed in the St-based MIH, indicating fewer pre-adsorbed water molecules were replaced per adsorption event. This supports the idea that the hydrophobic functional monomer enhances the imprinting quality by reducing the interference of the hydrophilic solvent in template/monomer complexation, leading to a well-defined imprint geometry for the template. Additionally, it facilitates BPA rebinding to the imprinted cavities by minimizing hindrance from pre-adsorbed water and/or promoted hydrophobic interactions. The higher degree of guest–host matching with St moieties is further supported by the higher adsorption heat released in the St-based MIH (ΔH°ads = −38.9 kJ/mol) compared to the MAA-based system (ΔH°ads = −35.2 kJ/mol).

Table 3. Thermodynamic Parameters of MIHs Prepared with Different Functional Monomers for Their Respective Bisphenol Templates.

MIH template T (K) ΔG°ads (kJ/mol) ΔH°ads (kJ/mol) ΔS°ads (J mol–1 K–1)
St-based BPA 298 –23.8 –38.9 –50.6
308 –23.3
318 –22.8
2BPF 298 –22.4 –6.4 53.9
318 –23.5
328 –24.1
4BPF 298 –19.7 14.1 112.2
318 –21.7
328 –22.6
MAA-based BPA 298 –23.1 –35.2 –40.5
308 –22.7
318 –22.3
2BPF 298 –20.6 16.1 123.1
318 –23.1
328 –24.3
4BPF 298 –21.0 –15.9 17.0
318 –21.4
328 –21.5

In contrast to BPA adsorption, 2BPF and 4BPF adsorptions by their corresponding MIHs took place with a weak driving force (ΔH°ads = −6.4 to −15.9 kJ/mol) or even required extra energy (ΔH°ads = 8.9–16.1 kJ/mol) to proceed. The positive ΔS°ads values of 2BPF and 4BPF adsorptions by their corresponding St- and MAA-based MIHs indicate replacement of multiple pre-adsorbed water molecules with one 2BPF or 4BPF adsorption. This behavior suggests weak complexation between these bisphenols with St or MAA monomers, leading to a low imprinting efficiency and quality. The hindered template/monomer complexation issue was more pronounced in the 4BPF/St and 2BPF/MAA systems, comprehensively resulting in endothermic adsorptions coupled with highly positive ΔS°ads values (112.2–123.1 J mol–1 K–1), low adsorption affinity (KL = 1.22–2.14 L/mg), low IF values (5.3–5.5), and Freundlich-closed adsorption behavior. Since all three bisphenols possess a similar molecular structure, the high imprinting performance with BPA could be attributed to its strong structural directing ability owing to its two additional -CH3 groups on the bridged carbon between its two phenyl moieties and p-OH groups.

3.4. Selectivity of MIHs for Different Bisphenols

Figure 5 illustrates the adsorption ability and selectivity of MIHs to the three bisphenols in the mixtures. The coexistence of structural analogues inhibited the adsorption of targets by their corresponding imprints. However, regardless of the types of imprints and functional monomers, BPA exhibited the highest competitive rebinding ability to the MIHs, with the order of binding ability being BPA > 2BPF > 4BPF (Figure 5a–c). Based on the adsorption behavior of bisphenols with different imprints, BPA has the potential to serve as a dummy template for 2BPF and 4BPF as BPA imprints exhibit comparable or even higher adsorption capacity for these analogues than their corresponding imprints. Similarly, 2BPF could act as a dummy template for BPA in the St-based system. The selectivity of MIHs for a templated target over analogues in the mixtures was evaluated based on the ratios of distribution coefficients between compounds (Kd, eq 5). Since the apparent adsorption of MIHs comprised both nonspecific adsorption by the matrix and specific adsorption by the imprints, a relative selectivity coefficient (k′, eq 3), derived from the ratio of the selectivity coefficient (k, eq 4) of a MIH (kMIH) to that of its corresponding NIH (kNIH), was calculated. This coefficient accounts for nonspecific interactions and provides a more accurate evaluation of the selectivity of the imprints. If k′ exceeds unity, this indicates that the imprints exhibit preferential binding toward the target compared to the analogues. The MIHs with BPA imprints all demonstrated high BPA selectivity (kBPA/analogues = 1.3–3.5) over 2BPF or 4BPF, and the selectivity varied with functional monomers. Analysis of variance indicates that the selectivity variations among functional monomers were statistically significant (p = 0.0108–0.0262 (Table S5)). While BPA selectivities over 2BPF and 4BPF were 2.3 and 1.3, respectively, in the MMA-based MIHs, they increased to 3.5 and 2.6, respectively, in the MAA-based MIHs (Figure 5d). This reveals that H-bonds with MAA moieties can effectively distinguish BPA, which has two p-OH groups, from 2BPF, which contains two o-OH groups. Moreover, the two -CH3 groups on the bridged carbon atom of BPA synergistically promote preferential BPA adsorption relative to 4BPF to the imprinted sites. The BPA selectivity over 4BPF further increased to 2.9 in the St-based MIHs. Compared to the statistical difference between the MAA- and MMA-based systems (p = 0.0611), this selectivity in the St-based system differs more significantly from that in the MMA-based system, with a p value of 0.0169 (Table S6), indicating that St moieties are more effective than MAA moieties in distinguishing BPA from 4BPF. In contrast to the high BPA-to-4BPF selectivity (2.9), BPA-to-2BPF selectivity decreased to 2.0. As the distinct molecular feature of 4BPF compared to BPA and 2BPF is the rotational flexibility of its two phenyl groups, the high degree of exclusion of 4BPF from the BPA imprints is attributed to hindered π–π interactions with the St moieties.38 Moreover, a stabilized molecular conformation is the key factor governing selectivity in the St-based system.

Figure 5.

Figure 5

Competitive adsorption of bisphenols by (a) St-based, (b) MAA-based, and (c) MMA-based MIHs and corresponding NIHs in a mixture containing the three bisphenols, each at an initial concentration of 20 mg/L. Selectivity of (d) BPA, (e) 2BPF, and (f) 4BPF imprints of MIHs with different functional monomers.

In contrast to BPA imprints, 2BPF and 4BPF imprints showed less selectivity toward their template compounds compared to BPA (k2BPF/BPA = 0.3–0.7, and k4BPF/BPA = 0.4–1.0) (Figure 5e,f). This finding suggests that the two -CH3 groups, two p-OH groups, and restricted molecular conformation of BPA not only benefit molecular imprinting but also facilitate its rebinding to the nanocavities. Despite the low target-to-BPA selectivity, the 2BPF imprints with St moieties were preferentially bound with 2BPF over 4BPF (k2BPF/4BPF = 2.8), while the 4BPF imprints in MMA-based MIHs bound the template molecule more competitively than 2BPF (k4BPF/2BPF = 1.7). These phenomena again support the unfavorable formation of H-bond and π–π interactions with 2BPF and 4BPF, respectively.

3.5. Intermolecular Interactions

3.5.1. Template/Monomer Complex

To determine whether the unique molecular configuration of BPA contributes to its superior structure-directing ability in imprinting and to ascertain the limitations of 2BPF and 4BPF in complexation with MAA/MMA and St monomers, respectively, intermolecular interactions between the functional monomers and the three bisphenols were analyzed using 1H NMR in DMSO-d6. Figure 6 illustrates the partial 1H NMR spectra of St, bisphenols, and the bisphenol/St mixtures with a controlled bisphenol:St molar ratio of 1:2. Upon complexation between St and bisphenols, upfield shifts of aromatic protons Hd–Hf of St were observed (Figure 6a–c), while the aromatic protons of all three bisphenols displayed downfield shifts (Figure 6d–f). The downfield and upfield shifts, resulting from deshielding and shielding effects, respectively, suggest aromatic donor–acceptor π–π interactions between St and the bisphenol molecules.39 The changes in chemical shifts (Δδ) of the aromatic protons of St, when associated with the three bisphenols individually, were recorded and are presented in Figure S3a. The largest upfield shifts in the BPA/St complex reveal the strongest interaction between the functional monomer and BPA, attributed to the presence of more electron-donating substituents on BPA (-CH2-(CH3)2) and more compatible π–π stacking conformations between the two molecules. Various π–π interaction geometries, such as face-to-face, parallel displaced, and edge-to-face arrangements, significantly influence the binding strength.40 To further identify the π–π stacking geometry, 1H–1H NOESY NMR analysis in DMSO-d6 was conducted for the three bisphenol/St complexes. As shown in Figure 6g, strong NOE cross-peaks were observed between the aromatic protons of St (Hd–Hf) and H3 of BPA, while H2 of BPA only correlated to He and Hf of St. This suggests a spatially close contact between the BPA and St (<4 Å) through face-to-face and/or parallel displaced π–π stacking interactions. For the 2BPF/St complex (Figure 6h), NOE cross-peaks between Hd–Hf of St and H4′ and H5′ of 2BPF, along with the chemical exchange-induced cross-peaks between H3′ of 2BPF and the aromatic protons of St, were observed. This suggests that the o-OH groups of 2BPF direct its phenyl groups to lean toward and contact the aromatic group of St. In contrast to BPA and 2BPF, only weak chemical exchange cross-peaks of H6 of 4BPF were found to correlate to Hf of St in the 4BPF/St complex (Figure 6i), suggesting an edge-to-face arrangement. The dissimilarity in bisphenol/St complexation geometries is associated with the chemical configuration of bisphenol molecules. The two bulky -CH3 groups on the bridged C atom restrict the rotation of the two phenyl groups in the BPA compound, thus facilitating the face-to-face complexation with styrene.38 Although 2BPF lacks the two -CH3 groups, its two adjacent o-OH groups still restrain the rotation of the two phenyl groups to a certain extent via an intramolecular H-bond to enable the π–π stacking.41 Unlike BPA and 2BPF, rotation of the phenyl groups is more profound in 4BPF due to absence of steric hindrance or intramolecular bonding.38 As a result, 4BPF exhibits the weakest imprinting ability in the St-based system.

Figure 6.

Figure 6

Partial 1H NMR spectra of (a–c) aromatic protons of styrene upon formation of complexes with bisphenols and aromatic protons of (d) BPA, (e) 2BPF, and (f) 4BPF upon formation of complexes with styrene. Partial 1H–1H NOESY NMR spectra of (g) BPA/St, (h) 2BPF/St, and (i) 4BPF/St complexes. The black arrows indicate aromatic protons of bisphenol/St NOE cross-peaks. The molar ratios of the bisphenol/St complexes were held at 1:2 in DMSO-d6. Full 1H NMR and 1H–1H NOESY NMR spectra are shown in Figures S4 and S5.

MAA is expected to interact with the three bisphenols through hydrogen bonds via its -COOH groups. To confirm this interaction, the 1H NMR spectra of MAA and the MAA complexed with the three bisphenols individually were acquired, as shown in Figure 7. It was observed that the -OH proton peak of BPA or 4BPF was broadened and diminished when interacting with MAA as a result of fast proton exchange between the -OH groups and the -COOH groups of MAA (Figure 7a,c).42 However, such a phenomenon was less prominent in the MAA/2BPF complex (Figure 7b). The -OH protons of MAA showed the largest Δδ value when complexing with BPA, while the shift was the smallest when sociating with 2BPF (Figure S3b). Correspondingly, stronger chemical exchange cross-peaks between MAA and BPA or 4BPF compared to the MAA/2BPF complex were observed in the 1H–1H NOESY NMR spectra (Figure 7d–f). These findings indicate that the interaction of MAA with the two most distant p-OH groups of BPA and 4BPF molecules is more favorable than the interaction with the o-OH groups in 2BPF due to weaker steric effects and minimized charge repulsion.41 The electrostatic attraction between MAA and BPA and 4BPF stabilizes their complexes, thus improving the imprinting quality of these two bisphenols. On the other hand, the hindered interaction between MAA and 2BPF during imprinting not only results in low imprinting quality but also leads to the endothermic adsorption of 2BPF by its imprints in the MAA-based system.

Figure 7.

Figure 7

Partial 1H NMR spectra of the (a) BPA/MAA, (b) 2BPF/MAA, and (c) 4BPF/MAA complexes. Partial 1H–1H NOESY NMR spectra of the (d) BPA/MAA, (e) 2BPF/MAA, and (f) 4BPF/MAA complexes. The black arrows indicate the chemical exchange cross-peaks at -OH protons of bisphenol/MAA complexes. The molar ratios of the bisphenol/MAA complexes were held at 1:2 in DMSO-d6. Full 1H NMR and 1H–1H NOESY NMR spectra are shown in Figures S6 and S7.

MMA molecules were found to interact with the three bisphenols via CH−π and H-bond interactions with their -OCH3 (Figure 8a–c) and C=O groups (Figure 8d–f), respectively, as shown in Figure 8. The CH−π interaction mainly occurred between the -OCH3 groups of MMA and the aromatic rings of the bisphenols (Figure 8g–i). Relative to the interactions with 2BPF and 4BPF, the CH−π interaction was stronger in the BPA/MMA complexes according to the large Δδ value of the -OCH3 protons (Figure 8a–c and Figure S3c). The polar attraction between the -OH groups of the bisphenols and the C=O group of MMA shifted the -OH proton peak to an upfield region (Figure 8d–f). Similar to the H-bond interactions with MAA molecules, BPA and 4BPF exhibited stronger H-bond interactions with MMA but not in the case of 2BPF. The H-bond and CH−π interactions stabilize the BPA/MMA complexes more effectively compared to 2BPF/MMA and 4BPF/MMA complexes, thus resulting in the highest IF for this template. However, despite these interactions, the low Langmuir-correlated adsorption of MMA-based MIHs (Table 2) indicates that the noncovalent interactions involving only MMA monomers are not as strong as the π–π and H-bond interactions with St and MAA monomers, respectively, in creating specific binding sites. Scheme 2 illustrates the different interactions between bisphenols and the monomers. Overall, the strong capability of BPA in directing monomers to achieve efficient and effective imprinting is comprehensively due to its two -CH3 groups on the bridged C atom, restricted rotation of the two phenyl groups, and two p-OH groups that are far apart. This configuration enables BPA to form stable complexes with monomers through π–π stacking, H-bonds, or weak van der Waals forces. As a result, more templates can be incorporated into the polymeric matrix to increase the adsorption capacity of MIHs. Meanwhile, polymerization along the shape of the template creates imprinted cavities that fit better with the BPA molecules.

Figure 8.

Figure 8

Partial 1H NMR spectra of (a–c) -OCH3 protons of MMA upon formation of complexes with bisphenols and -OH protons of (d) BPA, (e) 2BPF, (f) 4BPF upon formation of complexes with MMA. Partial 1H–1H NOESY NMR spectra of (g) BPA/MMA, (h) 2BPF/MMA, and (i) 4BPF/MMA complexes. The black arrows indicate bisphenol/MMA NOE cross-peaks. The molar ratios of bisphenol/MMA complexes were held at 1:2 in DMSO-d6. Full 1H NMR and 1H–1H NOESY NMR spectra are shown in Figures S8 and S9.

Scheme 2. Proposed Geometries of π–π Interactions between St and Bisphenols in (a) BPA/St, (b) 2BPF/St, and (c) 4BPF/St Complexes and H-Bond and CH−π Interactions of BPA with (d) MAA and (e) MMA Monomers.

Scheme 2

3.5.2. Template/Polymer Interactions

As mentioned above, BPA demonstrated the strongest competitive rebinding ability to MIHs while coexisting with the other two analogues, regardless of whether 2BPF or 4BPF served as the template. The distinguishing feature of BPA compared to 2BPF and 4BPF may lie in its two -CH3 substituents on the bridged carbon atom between the two phenyl groups, which not only restrict the rotation of the phenyl groups but also interact with copolymers via van der Waals forces. To further elucidate the exceptional BPA adsorption attributed to the -CH3 groups, we analyzed the association of the three bisphenols with p(St-co-MMA), p(MAA-co-MMA), and pMMA using 1H–1H NOESY NMR in CDCl3 or DMSO-d6. As illustrated in Figure 9a, a strong NOE cross-peak was observed between the -CH3 protons of BPA and the aromatic protons of the phenyl group in p(St-co-MMA), indicating the proximity of the -CH3 groups to the aromatic rings. While such CH−π interaction was also evident in the St/BPA complexes (Figure S10), it appeared to be more pronounced when BPA interacted with the copolymer because of a weaker steric effect compared to the π–π interaction. The CH−π interaction is a significant noncovalent attractive force to drive aromatic–aliphatic interactions for molecular recognition.4345 In this study, such a CH−π interaction could initially drive BPA to approach the imprinted site and then facilitate BPA to fit into the cavity. In contrast, no discernible NOE cross-peak was observed between the aromatic rings of the copolymer and the bridged -CH2 protons of 2BPF and 4BPF (Figure 9b,c). For interaction with the MAA-containing copolymer, the H-bond interaction between the -OH groups of BPA and the -COOH groups of the MAA moieties was still the dominant force that bound BPA to p(MAA-co-MMA) (Figure S12). In the absence of St or MAA moieties, the -CH3 groups and aromatic rings of BPA were found to interact with the -OCH3 groups of pMMA via a dispersion force and the CH−π interaction, respectively (Figure 10a,b). To validate these weak through-space interactions, 1H ROESY NMR analysis was further carried out owing to its enhanced sensitivity. The -OCH3 proton (ca. 3.6 ppm) of pMMA was selectively irradiated to observe its intermolecular interactions with the BPA molecules (Figure 10c). While the -OCH3 protons showed intermolecular interactions with the aromatic (ca. 6.7 and 7.1 ppm) and -CH3 protons (ca. 1.6 ppm) of BPA molecules, no observable ROE signals were detected for 2BPF and 4BPF molecules (Figure 10d,e).

Figure 9.

Figure 9

Partial 1H–1H NOESY NMR spectra of p(St-co-MMA) associated with (a) BPA (the black arrows indicate CH−π NOE cross-peaks), (b) 2BPF, and (c) 4BPF in CDCl3. Full 1H–1H NOESY NMR spectra are shown in Figure S11.

Figure 10.

Figure 10

(a and b) Partial 1H–1H NOESY NMR spectra of p(MMA) upon association with BPA in CDCl3. 1H ROESY NMR spectra of p(MMA) upon association with (c) BPA, (d) 2BPF, and (e) 4BPF in CDCl3. The -OCH3 proton of p(MMA) was selectively irradiated (the downward peak shown in green spectra at ca. 3.6 ppm) to observe the intermolecular interaction with bisphenol templates. Full 1H–1H NOESY NMR spectra are shown in Figure S13.

Based on the NMR characterizations, the intermolecular interactions between BPA and copolymers are illustrated in Scheme 3. The higher affinity of BPA over 2BPF and 4BPF for the MIHs stems also from its additional -CH3 substituents on the bridged carbon atom, p-OH groups, and restricted molecular conformation. The critical role of the -CH3 groups in promoting and stabilizing the binding interactions of BPA has been demonstrated in many biological activities.46,47 In this study, the pair of -CH3 groups enables BPA to additionally interact with MMA moieties via van der Waals forces in all of the copolymers. Moreover, they restrict the rotation of the two phenyl groups in BPA, facilitating the CH−π interaction between the -OCH3 group of the MMA moieties and the aromatic ring of BPA molecules.38 These additional interactions promote the competitive adsorption of BPA in all of the imprinted systems even though the imprinted sites are not customized for this compound. In contrast, the weakest rebinding ability of 4BPF in the competitive systems is presumably due to its rotating phenyl groups, which hinder its interaction with MIHs.

Scheme 3. Proposed Intermolecular Interactions between BPA and (a) p(St-co-MMA) and (b) p(MAA-co-MMA).

Scheme 3

4. Conclusions

The key molecular features of templates and functional monomers that govern the imprinting and rebinding ability of MIHs among three bisphenol analogues, BPA, 2BPF, and 4BPF, have been identified. Compared to hydrophilic MAA monomers, hydrophobic St monomers are more suitable for BPA imprinting as they inhibit the interference of a water/polar solvent during template/monomer complexation and target rebinding, thus enabling MIHs to exhibit high affinity for BPA. While functional monomers primarily influence the strength of binding of MIHs to the target, molecular configurations of templates comprehensively determine adsorption capacities, affinity, and selectivity. BPA has the strongest structural directing ability, compared to 2BPF and 4BPF, to achieve high imprinting efficiency and effectiveness for superior adsorption capacity and selectivity owing to its two additional -CH3 groups on the bridged carbon, p-OH groups, and restricted molecular conformation. These features also allow BPA to be more competitive in rebinding to the imprinted sites in the coexistence of the other two analogues even though the sites are created by structural analogues. In contrast, 4BPF is the least competitive to the binding sites, presumably due to its rotating phenyl groups. The rotational flexibility of 4BPF also limits its π–π interactions with St monomers, while the two o-OH groups of 2BPF hinder H-bond interactions with MAA monomers. The optimal template/functional monomer combinations for high adsorption performance include BPA/St, 2BPF/St, and 4BPF/MAA. Moreover, BPA has the potential to serve as a dummy template for 2BPF and 4BPF across the studied systems, while 2BPF can play a similar role for BPA in the St-based system.

Acknowledgments

The authors thank the National Science and Technology Council (NSTC), Taiwan, for financial support under Grants MOST 106-2628-E-009-005-MY3, NSTC 112-2221-E-A49-021, and NSTC 113-2221-E-A49-033-MY2. Additional support was provided by the Higher Education Sprout Project of National Yang Ming Chiao Tung University and the Ministry of Education (MOE), Taiwan.

Supporting Information Available

The Supporting Information is available free of charge at https://pubs.acs.org/doi/10.1021/acsami.5c03038.

  • Characterization details, including measurement of N2 adsorption–desorption isotherms, SEM, TEM, DLS, and LC-MS/MS; statistical analysis; calculation of imprinting factors; BET surface areas and pore volumes of the different MIHs and the corresponding NIHs; isotherm parameters of different functional monomer-based NIHs for bisphenols; supporting table for statistical analysis; SEM images of different functional monomer-based MIHs; N2 adsorption–desorption isotherm curves and pore size distributions; 1H NMR chemical shift changes (Δδ) of functional monomers after complexing with bisphenols; 1H NMR spectra of bisphenols and functional monomers before and after complexation; 1H–1H NOESY NMR spectra of bisphenol/functional monomer complexes; and 1H–1H NOESY NMR spectra of bisphenol/polymer complexes (PDF)

Author Contributions

K.-Z.C.: conceptualization, methodology, investigation, validation, analysis, visualization, and writing of the original draft. S.-m.C.: conceptualization, methodology, project administration, funding acquisition, supervision, and review and editing.

The authors declare no competing financial interest.

Supplementary Material

References

  1. den Braver-Sewradj S. P.; van Spronsen R.; Hessel E. V. S. Substitution of bisphenol A: a review of the carcinogenicity, reproductive toxicity, and endocrine disruption potential of alternative substances. Critical Reviews in Toxicology 2020, 50 (2), 128–147. 10.1080/10408444.2019.1701986. [DOI] [PubMed] [Google Scholar]
  2. Catenza C. J.; Farooq A.; Shubear N. S.; Donkor K. K. A targeted review on fate, occurrence, risk and health implications of bisphenol analogues. Chemosphere 2021, 268, 129273. 10.1016/j.chemosphere.2020.129273. [DOI] [PubMed] [Google Scholar]
  3. Liu J.; Zhang L.; Lu G.; Jiang R.; Yan Z.; Li Y. Occurrence, toxicity and ecological risk of Bisphenol A analogues in aquatic environment - A review. Ecotoxicology and Environmental Safety 2021, 208, 111481. 10.1016/j.ecoenv.2020.111481. [DOI] [PubMed] [Google Scholar]
  4. Yang Q.; Wu X.; Peng H.; Fu L.; Song X.; Li J.; Xiong H.; Chen L. Simultaneous phase-inversion and imprinting based sensor for highly sensitive and selective detection of bisphenol A. Talanta 2018, 176, 595–603. 10.1016/j.talanta.2017.08.075. [DOI] [PubMed] [Google Scholar]
  5. Wu X.; Wang X.; Lu W.; Wang X.; Li J.; You H.; Xiong H.; Chen L. Water-compatible temperature and magnetic dual-responsive molecularly imprinted polymers for recognition and extraction of bisphenol A. Journal of Chromatography A 2016, 1435, 30–38. 10.1016/j.chroma.2016.01.040. [DOI] [PubMed] [Google Scholar]
  6. Wang S.; Shao R.; Li W.; Li X.; Sun J.; Jiao S.; Dai S.; Dou M.; Xu R.; Li Q.; et al. Three-Dimensional Ordered Macroporous Magnetic Inverse Photonic Crystal Microsphere-Based Molecularly Imprinted Polymer for Selective Capture of Aflatoxin B1. ACS Appl. Mater. Interfaces 2022, 14 (16), 18845–18853. 10.1021/acsami.2c01014. [DOI] [PubMed] [Google Scholar]
  7. Chin K.-Z.; Chang S.-m. SiO2-Coated Molecularly Imprinted Copolymer Nanostructures for the Adsorption of Bisphenol A. ACS Applied Nano Materials 2019, 2 (1), 89–99. 10.1021/acsanm.8b01706. [DOI] [Google Scholar]
  8. Lasagabáster-Latorre A.; Cela-Pérez M. C.; Fernández-Fernández S.; López-Vilariño J. M.; González-Rodríguez M. V.; Abad M. J.; Barral-Losada L. F. Insight into BPA-4-vinylpyridine interactions in molecularly imprinted polymers using complementary spectroscopy techniques. Mater. Chem. Phys. 2013, 141 (1), 461–476. 10.1016/j.matchemphys.2013.05.045. [DOI] [Google Scholar]
  9. Alnaimat A. S.; Barciela-Alonso M. C.; Bermejo-Barrera P. Determination of bisphenol A in tea samples by solid phase extraction and liquid chromatography coupled to mass spectrometry. Microchemical Journal 2019, 147, 598–604. 10.1016/j.microc.2019.03.026. [DOI] [Google Scholar]
  10. Yu C.; Shan J.; Chen Y.; Shao J.; Zhang F. Preparation and adsorption properties of rosin-based bisphenol A molecularly imprinted microspheres. Materials Today Communications 2020, 24, 101076. 10.1016/j.mtcomm.2020.101076. [DOI] [Google Scholar]
  11. Gao Q.; Zang Y.; Xie J.; Wu Y.; Xue H. 4-Pentenoyl-isoleucyl-chitosan oligosaccharide and acrylamide functional monomer-dependent hybrid bilayer molecularly imprinted membrane for sensitive electrochemical sensing of bisphenol A. RSC Adv. 2021, 11 (58), 36769–36776. 10.1039/D1RA04924K. [DOI] [PMC free article] [PubMed] [Google Scholar]
  12. Wang H.; Wang H.; Bai Q.; Xu Y.; Bo C.; Gong B. Fabrication of molecularly imprinted resin via controlled polymerization applied in the enrichment of bisphenol A for plastic products. J. Sep. Sci. 2023, 46 (17), 2300206. 10.1002/jssc.202300206. [DOI] [PubMed] [Google Scholar]
  13. Cui Y.; Ding J.; Lin J.; Li Q.; Ding L. Cellulose-incorporated imprinted materials with amphiphilic crosslinking structure for selective adsorption of bisphenol A. Industrial Crops and Products 2022, 187, 115308. 10.1016/j.indcrop.2022.115308. [DOI] [Google Scholar]
  14. Lamaoui A.; María Palacios-Santander J.; Amine A.; Cubillana-Aguilera L. Computational approach and ultrasound Probe-Assisted synthesis of magnetic molecularly imprinted polymer for the electrochemical detection of bisphenol A. Materials Science and Engineering: B 2022, 277, 115568. 10.1016/j.mseb.2021.115568. [DOI] [Google Scholar]
  15. Cai W.; Xu D.; Qian L.; Wei J.; Xiao C.; Qian L.; Lu Z.-y.; Cui S. Force-Induced Transition of π-π Stacking in a Single Polystyrene Chain. J. Am. Chem. Soc. 2019, 141 (24), 9500–9503. 10.1021/jacs.9b03490. [DOI] [PubMed] [Google Scholar]
  16. Adamovic I.; Li H.; Lamm M. H.; Gordon M. S. Modeling Styrene-Styrene Interactions. J. Phys. Chem. A 2006, 110 (2), 519–525. 10.1021/jp058140o. [DOI] [PubMed] [Google Scholar]
  17. Zhang Y.; Song D.; Lanni L. M.; Shimizu K. D. Importance of Functional Monomer Dimerization in the Molecular Imprinting Process. Macromolecules 2010, 43 (15), 6284–6294. 10.1021/ma101013c. [DOI] [Google Scholar]
  18. Li C.; Yuan J.; Wang C.; Wei Y. Molecular bottlebrush polymer modified magnetic adsorbents with high physicochemical selectivity and unique shape selectivity. Journal of Chromatography A 2018, 1564, 16–24. 10.1016/j.chroma.2018.06.019. [DOI] [PubMed] [Google Scholar]
  19. Yuan W.; Zhou L.; Zhang Z.; Ying Y.; Fan W.; Chai K.; Zhao Z.; Tan Z.; Shen F.; Ji H. Synergistic dual-functionalities of starch-grafted-styrene hydrophilic porous resin for efficiently removing bisphenols from wastewater. Chemical Engineering Journal 2022, 429, 132350. 10.1016/j.cej.2021.132350. [DOI] [Google Scholar]
  20. Liu Y.; Wang D.; Du F.; Zheng W.; Liu Z.; Xu Z.; Hu X.; Liu H. Dummy-template molecularly imprinted micro-solid-phase extraction coupled with high-performance liquid chromatography for bisphenol A determination in environmental water samples. Microchemical Journal 2019, 145, 337–344. 10.1016/j.microc.2018.10.054. [DOI] [Google Scholar]
  21. Zhang B.; Fan X.; Zhao D.. Computer-Aided Design of Molecularly Imprinted Polymers for Simultaneous Detection of Clenbuterol and Its Metabolites. In Polymers; 2019; Vol. 11. [DOI] [PMC free article] [PubMed]
  22. Wang L.; Liu Q.; Zou Y.; Liu S.; Yang Y.; Tao Y.; Wang M.; Li L.; Wang D.; Gao D. Magnetic molecular imprinted covalent organic framework composite for the magnetic solid-phase extraction of bisphenol AF. Journal of Chromatography A 2024, 1717, 464693. 10.1016/j.chroma.2024.464693. [DOI] [PubMed] [Google Scholar]
  23. Chen R.-N.; Kang S.-H.; Li J.; Lu L.-N.; Luo X.-P.; Wu L. Comparison and recent progress of molecular imprinting technology and dummy template molecular imprinting technology. Analytical Methods 2021, 13 (39), 4538–4556. 10.1039/D1AY01014J. [DOI] [PubMed] [Google Scholar]
  24. Zhan W.; Wei F.; Xu G.; Cai Z.; Du S.; Zhou X.; Li F.; Hu Q. Highly selective stir bar coated with dummy molecularly imprinted polymers for trace analysis of bisphenol A in milk. J. Sep. Sci. 2012, 35 (8), 1036–1043. 10.1002/jssc.201101016. [DOI] [PubMed] [Google Scholar]
  25. Li J.; Zhou H.; Liu Y.-X.; Yan X.-Y.; Xu Y.-P.; Liu S.-M. Solid-phase extraction for selective determination of bisphenol A in drinks and fruits by dummy surface molecularly imprinted polymer with direct synthetic method. Food Additives & Contaminants: Part A 2014, 31 (6), 1139–1146. 10.1080/19440049.2014.906751. [DOI] [PubMed] [Google Scholar]
  26. Lin Z.; Cheng W.; Li Y.; Liu Z.; Chen X.; Huang C. A novel superparamagnetic surface molecularly imprinted nanoparticle adopting dummy template: An efficient solid-phase extraction adsorbent for bisphenol A. Anal. Chim. Acta 2012, 720, 71–76. 10.1016/j.aca.2012.01.020. [DOI] [PubMed] [Google Scholar]
  27. Liu R.; Feng F.; Chen G.; Liu Z.; Xu Z. Barbell-shaped stir bar sorptive extraction using dummy template molecularly imprinted polymer coatings for analysis of bisphenol A in water. Anal. Bioanal. Chem. 2016, 408 (19), 5329–5335. 10.1007/s00216-016-9628-3. [DOI] [PubMed] [Google Scholar]
  28. Wang Y.; Tian M.; Yu K.; Li L.; Zhang Z.; Li L. A versatile strategy to fabricate magnetic dummy molecularly imprinted mesoporous silica particles for specific magnetic separation of bisphenol A. New J. Chem. 2019, 43 (8), 3400–3408. 10.1039/C8NJ06027D. [DOI] [Google Scholar]
  29. Prete M. C.; Dos Santos D. M.; Effting L.; Tarley C. R. T. Preparation of Molecularly Imprinted Poly(methacrylic acid) Grafted on Iniferter-Modified Multiwalled Carbon Nanotubes by Living-Radical Polymerization for 17β-Estradiol Extraction. Journal of Chemical & Engineering Data 2019, 64 (5), 1978–1990. 10.1021/acs.jced.8b01010. [DOI] [Google Scholar]
  30. Wang F.; Guo L.; Qiu T.; Ye J.; He L.; Li X. A direct polymerization approach toward hindered phenol/polymer composite latex and its application for waterborne damping coating. Prog. Org. Coat. 2019, 130, 1–7. 10.1016/j.porgcoat.2019.01.032. [DOI] [Google Scholar]
  31. Niu J.; Liu H.; Wang X.; Wu D. Molecularly Imprinted Phase-Change Microcapsule System for Bifunctional Applications in Waste Heat Recovery and Targeted Pollutant Removal. ACS Appl. Mater. Interfaces 2019, 11 (41), 37644–37664. 10.1021/acsami.9b11856. [DOI] [PubMed] [Google Scholar]
  32. Dai J.; Tian S.; Jiang Y.; Chang Z.; Xie A.; Zhang R.; Li C.; Yan Y. Fe3C/Fe/C Magnetic Hierarchical Porous Carbon with Micromesopores for Highly Efficient Chloramphenicol Adsorption: Magnetization, Graphitization, and Adsorption Properties Investigation. Ind. Eng. Chem. Res. 2018, 57 (10), 3510–3522. 10.1021/acs.iecr.7b05300. [DOI] [Google Scholar]
  33. Yao M.; Liang C.; Yao S.; Liu Y.; Zhao H.; Qin C. Kinetics and Thermodynamics of Hemicellulose Adsorption onto Nanofibril Cellulose Surfaces by QCM-D. ACS Omega 2021, 6 (45), 30618–30626. 10.1021/acsomega.1c04391. [DOI] [PMC free article] [PubMed] [Google Scholar]
  34. Ghosal P. S.; Gupta A. K. Determination of thermodynamic parameters from Langmuir isotherm constant-revisited. J. Mol. Liq. 2017, 225, 137–146. 10.1016/j.molliq.2016.11.058. [DOI] [Google Scholar]
  35. Dauenhauer P. J.; Abdelrahman O. A. A Universal Descriptor for the Entropy of Adsorbed Molecules in Confined Spaces. ACS Central Science 2018, 4 (9), 1235–1243. 10.1021/acscentsci.8b00419. [DOI] [PMC free article] [PubMed] [Google Scholar]
  36. Hasanpour M.; Hatami M. Application of three dimensional porous aerogels as adsorbent for removal of heavy metal ions from water/wastewater: A review study. Adv. Colloid Interface Sci. 2020, 284, 102247. 10.1016/j.cis.2020.102247. [DOI] [PubMed] [Google Scholar]
  37. Huang P.; Xia D.; Kazlauciunas A.; Thornton P.; Lin L.; Menzel R. Dye-Mediated Interactions in Chitosan-Based Polyelectrolyte/Organoclay Hybrids for Enhanced Adsorption of Industrial Dyes. ACS Appl. Mater. Interfaces 2019, 11 (12), 11961–11969. 10.1021/acsami.9b01648. [DOI] [PubMed] [Google Scholar]
  38. Dávalos J. Z.; Herrero R.; Costa J. C. S.; Santos L. M. N. B. F.; Liebman J. F. Energetic and Structural Study of Bisphenols. J. Phys. Chem. A 2014, 118 (20), 3705–3709. 10.1021/jp503567c. [DOI] [PubMed] [Google Scholar]
  39. Lin C.; Skufca J.; Partch R. E. New insights into prediction of weak π-π complex association through proton-nuclear magnetic resonance analysis. BMC Chemistry 2020, 14 (1), 66. 10.1186/s13065-020-00718-x. [DOI] [PMC free article] [PubMed] [Google Scholar]
  40. Sinnokrot M. O.; Sherrill C. D. Highly Accurate Coupled Cluster Potential Energy Curves for the Benzene Dimer: Sandwich, T-Shaped, and Parallel-Displaced Configurations. J. Phys. Chem. A 2004, 108 (46), 10200–10207. 10.1021/jp0469517. [DOI] [Google Scholar]
  41. Bian C.; Li Y.; Wang S.; Jing X. Initial reaction mechanism between HO· and bisphenol-F: Conformational dependence and the role of nonbond interactions. Int. J. Quantum Chem. 2017, 117 (6), e25342 10.1002/qua.25342. [DOI] [Google Scholar]
  42. Hasani M.; Nordstierna L.; Martinelli A. Molecular dynamics involving proton exchange of a protic ionic liquid-water mixture studied by NMR spectroscopy. Phys. Chem. Chem. Phys. 2019, 21 (39), 22014–22021. 10.1039/C9CP03563J. [DOI] [PubMed] [Google Scholar]
  43. Cho K. H.; Yoon J. W.; Lee J. H.; Kim J. C.; Jo D.; Park J.; Lee S.-K.; Kwak S. K.; Lee U. H. Design of Pore Properties of an Al-Based Metal-Organic Framework for the Separation of an Ethane/Ethylene Gas Mixture via Ethane-Selective Adsorption. ACS Appl. Mater. Interfaces 2023, 15 (25), 30975–30984. 10.1021/acsami.3c03971. [DOI] [PubMed] [Google Scholar]
  44. Wang Y.; Yang Y.; Liu X.; Zhao J.; Liu R.; Xing B. Interaction of Microplastics with Antibiotics in Aquatic Environment: Distribution, Adsorption, and Toxicity. Environ. Sci. Technol. 2021, 55 (23), 15579–15595. 10.1021/acs.est.1c04509. [DOI] [PubMed] [Google Scholar]
  45. Li M.; Qing G.; Xiong Y.; Lai Y.; Sun T. CH-π Interaction Driven Macroscopic Property Transition on Smart Polymer Surface. Sci. Rep. 2015, 5 (1), 15742. 10.1038/srep15742. [DOI] [PMC free article] [PubMed] [Google Scholar]
  46. Okada H.; Tokunaga T.; Liu X.; Takayanagi S.; Matsushima A.; Shimohigashi Y. Direct Evidence Revealing Structural Elements Essential for the High Binding Ability of Bisphenol A to Human Estrogen-Related Receptor-γ. Environ. Health Perspect. 2008, 116 (1), 32–38. 10.1289/ehp.10587. [DOI] [PMC free article] [PubMed] [Google Scholar]
  47. Sui Y.; Ai N.; Park S.-H.; Rios-Pilier J.; Perkins J. T.; Welsh W. J.; Zhou C. Bisphenol A and Its Analogues Activate Human Pregnane X Receptor. Environ. Health Perspect. 2012, 120 (3), 399–405. 10.1289/ehp.1104426. [DOI] [PMC free article] [PubMed] [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Supplementary Materials


Articles from ACS Applied Materials & Interfaces are provided here courtesy of American Chemical Society

RESOURCES