Abstract
Conventional molecularly imprinted polymers (MIP)–based electrochemical sensors are generally susceptible to the changes of personal operation, electrode surface, and solution conditions. Herein, a ratiometric strategy was employed through introducing Cu2O nanoparticles (NPs) as inner reference probe to realize the reliable detection of diethylstilbestrol (DES). MIP film was prepared by electropolymerization of 1H-pyrrole-3-carboxylicacid in the presence of DES on carbon nanotubes/cuprous oxide/titanium carbide (CNT/Cu2O NPs/Ti3C2Tx) modified electrodes. The Ti3C2Tx with accordion-like structure not only possessed good electrical conductivity, but also facilitated the immobilization of Cu2O NPs, which contributed to stabilizing the signal. CNT was introduced to further improve the sensitivity of the sensor. Under optimum conditions, the MIP/CNT/Cu2O NPs/Ti3C2Tx electrochemical sensors showed a broad linear response range of 0.01 to 70 μM, and a low detection limit of 6 nM (S/N = 3). Moreover, the sensor was applied to detect DES in real samples including lake water, milk, and pork, and the recoveries for spiked standard were 88–112%. Thus, this work provides a new way for reliable DES detection.
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Introduction
Diethylstilbestrol (DES) is a representative kind of synthetic exogenous estrogen which is often used as the animal growth promoter and widely applied in veterinary medicine to treat estrogen deficiency [1]. However, DES can be absorbed by human body through food chain and combined with estrogen receptor, competing with endogenous estradiol, resulting in the disorder of human hormones and endocrine system [2]. Compared with the natural estrogen, DES is more stable and can stay in the human body for a long time, relevant researches manifest that DES can cause cancer [3]. DES has been prohibited by China, the USA, Japan, and the European Union for all food animals [4]. Therefore, monitoring the content of DES existing in the environment and foods (e.g., milk, meat) is of great significance. Various detection techniques including high-performance liquid chromatography [5], gas chromatography coupled with mass spectrometry [6], capillary electrochromatography [7], enzyme-linked immunosorbent assay [8], and immunoassay [9] have been applied to detect DES. However, these methods are either time-consuming or expensive. Electrochemical method has aroused widespread concern of researches for its easy operation and fast detection [10, 11].
Numerous researches have reported on the electrochemical detection of DES [12, 13]. For example, Yang et al. determined DES using a CeO2 nanorod/graphene nanoplatelet-modified electrode, with a low limit of detection of 1.5 nM [12]. In another report, DES was determined based on its electrochemical oxidation on a Cu-MOF–modified carbon paste electrode, the limit of detection was 2.7 nM [13]. However, such electrochemical sensors typically distinguish interferences by oxidation potential, so the selectivity is easily affected when the oxidation potential of interferences are close to DES. Therefore, to further improve the selectivity of electrochemical senor of DES is significant.
Molecularly imprinted polymers (MIP), as the bio-mimic material for selective recognition, have been widely applied to improve the selectivity of electrochemical sensors [14]. However, the response of MIP electrochemical sensor toward target is easily disturbed by the unavoidable factors, including the variations in the fabrication process of electrodes and the pollution of electrode surface [15, 16]. Fortunately, the ratiometric sensing strategy can effectively reduce the fluctuation of output signal [17], as the inner reference signal can correct the influence of various factors by using the ratio of the detection signal and inner reference signal as output signal. Therefore, ratiometric MIP electrochemical sensor can provide more reliable data with satisfactory selectivity. But so far, only a few researches on ratiometric molecularly imprinted electrochemical sensor have been reported [16, 18].
However, the immobilization process of inner reference substances (e.g., ferrocene and thionine) on electrode surface is complex, and usually involves electropolymerization or covalent coupling, which limited the application of ratiometric electrochemical sensor [19]. For this reason, it is of great significance to choose an appropriate inner reference to simplify the electrode modification process. Recently, it has been reported that Cu2O nanoparticles (NPs) show an oxidation peak at about − 0.1 V (vs. Ag/AgCl) in a pH 7.0 phosphate-buffer solution (PBS) and are used as the inner reference probe for the ratiometric detection of prostate specific antigen [20]. What is more, Cu2O NPs are facile to prepare and display stable electrochemical activity.
MXene is a new family of two-dimension (2D) materials consisting of the transition metal nitrides/carbides/carbonitrides with the general formula of Mn + 1XnTx (n = 1, 2, or 3), where the M, X, and T stand for early transition metal, carbon, or/and nitrogen and the surface terminal groups (e.g., − O, − OH, − F), respectively [21]. Due to the excellent electrical conductivity, high specific surface area and hydrophilicity, MXene has aroused great attention of analysts [22]. Ti3C2Tx is one of the representative materials of MXene, and is gradually applied to the field of electrochemical detection. For instance, alkalized Ti3C2Tx/MOF derived porous carbon composite was used as the modified material of electrode to monitor hydroquinone and catechol [23]. Park’s group reported a Ti3C2Tx/MWCNT-modified flexible electrochemical sensor for the detection of Cu2+ and Zn2+ in human biofluids [24]. The previously reported work manifest that MXene can provide the in situ growth sites for Fe3O4 NPs, and its unique accordion-like structure facilitates the dispersion and immobilization of Fe3O4 NPs [25]. Inspired by this, Cu2O NPs/Ti3C2Tx composite can also be prepared in a similar method because Ti3C2Tx shows good adsorption capacity toward heavy metallic ion (e.g., Pb2+, Cu2+) [24, 26].
Herein, ratiometric strategy was combined with MIP electrochemical sensor based on CNT/Cu2O NPs/Ti3C2Tx composite to detect DES. Cu2O NPs was loaded on Ti3C2Tx and used as an inner reference probe; CNT was introduced to increase the electrode surface and improve electrical conductivity. Finally, the MIP electrochemical sensor was prepared through the electropolymerization of 1H-pyrrole-3-carboxylicacid (py-3-COOH) in the presence of DES. The resulting ratiometric MIP electrochemical sensor (MIP/CNT/Cu2O NPs/Ti3C2Tx/GCE) showed a satisfactory linear relationship and low detection limit for DES detection. Compared to the non-ratiometric MIP electrochemical sensor, the output signal fluctuation of the ratiometric MIP electrochemical sensor was much smaller. The sensor was successfully applied to determine DES in spiked real samples including lake water, milk, and pork.
Experimental
Preparation of CNT/Cu 2 O NPs/Ti 3 C 2 T x composite
Accordion-like Ti3C2Tx was prepared by etching the precursor Ti3AlC2 with HF according to previous reports with subtle modification [25].
Cu2O NPs/Ti3C2Tx composite was synthesized by in situ growth of Cu2O NPs between the interlayers of accordion-like Ti3C2Tx. Briefly, 9 mg CuCl2·H2O was added into 50 mL of 0.2-mg mL− Ti3C2Tx dispersion and was ultrasonically treated for 30 min. Then, 0.4 mL of 0.5-M N2H4·H2O solution was rapidly injected into the above dispersion and vigorously stirred for 15 min. The precipitation was obtained by centrifugation and washed with deionized water for three times, and dried overnight at 45 °C.
CNT/Cu2O NPs/Ti3C2Tx composite was obtained through the self-assembly method. CNT dispersion was firstly prepared by dispersing 1-mg CNT into 1 mL of 0.2-mg mL−1 CTAB solution under ultrasound for 2 h. Subsequently, 1 mL of 2 mg mL−1 Cu2O NPs/Ti3C2Tx composite dispersion was added and sonicated for 30 min. The mixture was centrifugated and rinsed with deionized water for five times, dried for 24 h at 45 °C. The procedure of preparing CNT/Cu2O NPs/Ti3C2Tx composite is illustrated in Scheme 1 A.
Fabrication of MIP/CNT/Cu 2 O NPs/Ti 3 C 2 T x /GCE
Bare GCEs were polished with 0.05-μm Al2O3 aqueous slurry and cleaned with deionized water under ultrasonic conditions. Then, 5 μL of CNT/Cu2O NPs/Ti3C2Tx composite (1 mg mL−1) suspension was dropped on the cleaned GCE and dried at room temperature. The MIP film was synthesized by cyclic voltammetry (CV). The potential range was 0 ~ 0.8 V, the cycling number was 12 at a scan rate of 50 mV s−1, and the solution was 0.1 − M PBS (pH 7.0) containing 2.4-mM py-3-COOH, 0.6-mM DES, and 0.1-M KCl. The templates were removed in 0.1-M NaOH/alcohol solution (V/V, 1:1) under stirring for 10 min. For comparison, non-imprinted polymer (NIP) was prepared by the same procedure but without DES. The preparation process of MIP/CNT/Cu2O NPs/Ti3C2Tx/GCE is shown in Scheme 1 B.
Electrochemical measurements
The modified electrodes were characterized by CV and electrochemical impedance spectroscopy (EIS) in a mixed solution containing 5-mM K3[Fe(CN)6]/K4[Fe(CN)6] and 0.1-M KCl. CV tests were performed in the potential range of − 0.2 V ~ 0.6 V at 100 mV/s. Parameters for EIS measurements were as follows: applied potential, 0.18 V; amplitude, 0.005 V; high frequency, 105 Hz; low frequency, 1 Hz. Differential pulse voltammetry (DPV) was applied to detect DES. The details were as follows: potential range, − 0.4 V ~ 0.4 V; amplitude, 50 mV; pulse width, 0.05 s; sample width, 0.0167 s; pulse period, 0.2 s.
Preparation of real samples
The water samples were collected from Wuhan East Lake and spiked with of DES standard solutions (1 mL) at different concentration levels, then filtered with Φ = 0.22-μm nylon membrane. The milk and pork samples were bought from a local supermarket. Before measurement, the milk samples were mixed with 1 mL of DES standard solutions of different concentrations, then they were added into 20-mL alcohol and shaken for 15 min. After centrifuging at 10,000 rpm for 10 min, the supernatant was filtered with 0.22-μm nylon membrane and diluted to 50 mL with 0.1-M PBS (pH 7.5). As to pork samples, 4-g minced pork samples were spiked with 1 mL of DES standard solutions in a variety of concentrations; the mixture was transferred into 20-mL acetonitrile (contains 5% glacial acetic acid) and vigorously shaken for 15 min, followed by centrifugation at 10,000 rpm for 10 min. Then, the supernatant was extracted with 5 mL of n-hexane. Finally, the n-hexane layer was discarded, and the rest liquid was filtered with 0.22-μm nylon membrane and diluted to 50 mL with 0.1-M PBS (pH 7.5).
Results and discussion
Characterization of CNT/Cu 2 O NPs/Ti 3 C 2 T x composite
The morphologies of composites were characterized by SEM and TEM. As could be seen in Fig. 1A, bulk Ti3AlC2 is closely aligned and layered. After treatment with HF solution, it became an accordion-like multi-layer structure, because the Al layers were selectively removed from the Ti3AlC2 phase using HF solution (Fig. 1B). As shown in Fig. 1C, Cu2O NPs grow upon the surfaces and interlayers of Ti3C2Tx. This was related to the electrostatic and coordinated interaction between negative charged Ti3C2Tx and Cu2+ [27]. In Fig. 1D, CNTs were coated on the surface of Cu2O NPs/Ti3C2Tx after the self-assemble treatment. As exhibited in Fig. 1E, the film forms on the surface of CNT/Cu2O NPs/Ti3C2Tx composite after the electropolymerization of py-3-COOH in the presence of DES. Figure 1F shows parts of Cu2O NPs are agglomerated due to the high surface energy of Cu2O NPs, and the interplanar space of Ti3C2Tx is 1.02 nm (inserted HRTEM image in Fig. 1F).
The preparation procedures of CNT/Cu2O NPs/Ti3C2Tx composite were also characterized by XRD. As shown in Fig. 2A, the characteristic diffraction peaks at 9.5° and 38.9° correspond to the (002) and (104) planes of Ti3AlC2, respectively. The curve b exhibited that the 38.9° peak disappeared while the 9.5° peak shifted to 8.9°, for the removal of Al phase from Ti3AlC2. The movement of (002) peak was in agreement with the HRTEM result; d-spacing of the as-prepared Ti3C2Tx was wider than that of Ti3AlC2 (d = 0.93 nm) [28]. This manifested Ti3C2Tx was prepared successfully. In curve c, diffraction peaks at 36.2 and 42.1° corresponded to the (111) and (200) lattice planes of Cu2O NPs, respectively. The (002), (111), and (200) lattice planes appeared after the decoration of Ti3C2Tx with Cu2O NPs (curve d). In curve e, the diffraction intensity of Ti3C2Tx and Cu2O NPs decreased after the introduction of CNT. As shown in Fig. 2B, the zeta potential of the CNT/CTAB (1 mg mL−1 CNT dispersion containing 0.2 mg mL−1 CTAB) is measured to be + 40.1 mV. Therefore, electrostatic interaction must lead to the self-assembly of CNT and Cu2O NPs/Ti3C2Tx. In addition, XPS results indicated the successful preparation of CNT/Cu2O NPs/Ti3C2Tx (Fig. S1).
Electrochemical characterization of the modified electrode
The EIS was used to characterize the interface change after every modification steps of the electrode. The diameter of the semicircle decreased after the Cu2O NPs/GCE was successively modified with Ti3C2Tx and CNT (Fig. 3A) due to the introduction of Ti3C2Tx and CNT with good electrical conductivity. The electron transfer resistance (Ret) became large drastically after the polymerization of py-3-COOH in the presence of DES indicating the MIP film had poor conductivity. The Ret decreased after removing the DES from the MIP film as the binding cavities facilitated the probe to pass through the MIP films. However, when the MIP/CNT/Cu2O NPs/Ti3C2Tx/GCE was incubated in PBS containing DES, Ret increased for the blocking of binding sites. CV measurements were also conducted, and the results agreed with the EIS data (Fig. S2).
To illustrate the specific adsorption of MIP, DPV curves of MIP and NIP-modified CNT/Cu2O NPs/Ti3C2Tx/GCE before and after incubation in 50-μM DES were presented (Fig. 3B). The peaks at − 0.11 V and 0.14 V were assigned to Cu2O NPs and DES, respectively. The IDES increased while the ICu2O decreased after the rebinding of DES. The reason was that the cavities of MIP film were occupied by DES which led to the partial block of electron transfer channel toward Cu2O NPs, thus the signal of Cu2O NPs decreased. However, the ICu2O for NIP film almost remained unchanged after the incubation of DES, indicating there were no cavities formed in the NIP film (curve c and curve d).
Optimization of the experiment conditions
To improve the analytical capacity of the as-prepared MIP electrochemical sensor, optimization of experiment conditions including the molar ratio of monomer to template, polymerization cycles, pH, and incubation time were performed.
Polymer structure and rebinding capacity of MIP sensors were influenced by the monomer/template ratio. As shown in Fig. S3A, the value of IDES/ICu2O increases with the increase of py-3-COOH/DES ratio, for the formed MIP film becomes denser and has more imprinted cavities. However, py-3-COOH/DES ratio higher than 4:1 would also lead to the decrease of IDES/ICu2O, because the recognition sites were blocked by excess py-3-COOH. Therefore, the optimum ratio of py-3-COOH/DES was 4:1.
The thickness of MIP film greatly affected the number of recognition sites, which could be adjusted by changing the polymerization cycles. Thinner MIP film could not provide enough recognition sites, while the thicker MIP film was unfavorable for the removal of DES. The MIP film with the optimum thickness was obtained through 12 polymerization cycles (Fig. S3B).
The influence of pH on the sensing response was investigated from 6.0 to 8.5 (Fig. S3C). The IDES/ICu2O value increased as the pH increased from 6 to 7.5, the electro-oxidization reaction of DES was boosted at low acidity for the protons of DES were released in this process. At pH 7.5, the IDES/ICu2O value was the highest. When pH further increased, the IDES/ICu2O value decreased when the pH further increased, which might result from the dissociation of DES in alkaline solution [29].
Linear relationships between the oxidation potential of DES and Cu2O NPs and pH are shown in Fig. S3D;, their slopes were calculated to be − 52.3 mV and − 54.1 mV, respectively. It manifested that the number of electrons and protons involved in the redox of DES and Cu2O NPs was the same.
The optimum incubation time is 5 min according to Fig. S2E.
Stability of ratiometric electrochemical sensor
Robustness of inner reference signal is essential to the ratiometric electrochemical sensor. Here, DPV curves of CNT/Cu2O NPs/Ti3C2Tx/GCE in PBS (pH 7.5) for ten consecutive tests were basically the same; the oxidation peak of Cu2O remained constant (Fig. 4A). The signal stability of Cu2O NPs/GCE and Cu2O NPs/Ti3C2Tx/GCE was also explored. The results illustrated that the incorporation of Ti3C2Tx could effectively stabilize the response of the Cu2O NPs (Fig. S4). To illustrate the stability of the output signal of the as-prepared ratiometric electrochemical sensor, the DPV curves of three different MIP/CNT/Cu2O NPs/Ti3C2Tx/GCE were recorded after incubation (Fig. 4B). The ratio values of IDES/ICu2O almost remained unchanged while the values of IDES fluctuate greatly. To further verify the advantage of ratiometric strategy, the IDES and IDES/ICu2O data were collected and compared after ten paralleled tests were conducted with MIP/CNT/Cu2O NPs/Ti3C2Tx/GCE (Fig. 4C). The RSD of non-ratiometric sensor was 8.5% while that of the ratiometric sensor was 3.3%. This showed that the introduction of ratiometric strategy reduced the error caused by personal manipulation and changes in the surface of electrode, which helped to obtain more reliable data.
Analytical performance of ratiometric electrochemical sensor
The performance of MIP/CNT/Cu2O NPs/Ti3C2Tx/GCE was evaluated through DPV technique under optimized conditions. The MIP/CNT/Cu2O NPs/Ti3C2Tx/GCE was incubated in 0.1-M PBS (pH 7.5) containing different concentrations of DES. As depicted in Fig. 5A, the peak current of Cu2O NPs decreases, while the peak current of DES increases with the increase of DES concentration. The sensor showed a good linear relationship between IDES/ICu2O and CDES in the range from 0.01 to 70 μM (Fig. 5B). The linear equation was IDES/ICu2O = 0.0183 × CDES + 0.00502 (R2 = 0.9928), and the limit of detection (S/N = 3) was calculated to be 6 nM.
Selectivity, repeatability and lifetime
To investigate the selectivity of MIP/CNT/Cu2O NPs/Ti3C2Tx/GCE, the analogs of DES (i.e., E1, E2, BPA, BPS, and TBBPA) were chosen as the interference substances. The concentrations of DES and interference substances were 30 μM and 300 μM, respectively. As shown in Fig. 6A, the deviation of the IDES/ICu2O values are lower than 5.8%, indicating that the MIP/CNT/Cu2O NPs/Ti3C2Tx/GCE possesses satisfactory selectivity toward DES. The reason was that DES could be selectively adsorbed by the MIP film through hydrogen bond and the spatial structure matching between DES and imprinted cavities (Fig. 6B).
The repeatability was evaluated by five consecutive measurements of 50-μM DES using one electrode. The RSD value of IDES/ICu2O was 4.3%, indicating the satisfactory repeatability of the as-prepared electrode.
To research the lifetime, the as-prepared electrodes which had been stored at 4 °C for 3 weeks were applied to detect 50-μM DES in PBS (pH = 7.5). The value of IDES/ICu2O is only 5.3% lower than that of the initial detection. The results showed the as-prepared electrodes possessed good stability.
As shown in Table 1, although the immunosensors exhibit lower limit of detection, they are generally disposable, whereas the as-prepared MIP sensor in this work can be reused. Furthermore, the immunosensors are expensive and take a long time for analysis. Compared with the electrochemical sensors without a specific recognition device (Table 1), which typically distinguish interferences by potential, as described in the “Introduction”, the as-prepared MIP sensor in this work not only shows a lower limit of detection but also possesses good selectivity.
Analysis of real samples
To evaluate its practical analytic performance, the as-prepared sensor was applied to determine DES in real samples, including lake water, milk, and pork. As shown in Table 2, there no DES were found in the pretreated real samples using the as-prepared sensor and HPLC. After that, the real samples were spiked at three concentration levels (0.05 μM, 0.1 μM, and 1 μM). The recoveries of the spiked samples were 88–112%, and the RSD ranged from 3.6 to 5.5%. In order to verify the results obtained by the as-prepared sensor, HPLC measurements of the spiked real sample solutions were performed; it manifested that the concentrations detected by the as-prepared sensor were close to HPLC detection results. Therefore, the MIP/CNT/Cu2O NPs/Ti3C2Tx/GCE exhibited good practicality for DES detection in real samples.
Conclusions
In this work, we developed a ratiometric MIP electrochemical sensor for diethylstilbestrol detection based on the CNT/Cu2O NPs/Ti3C2Tx composite using the Cu2O NPs as the inner reference. The accordion-like structure of Ti3C2Tx was beneficial to the in situ growth and fixation of Cu2O NPs, resulting in the increase of signal stability of Cu2O NPs. Furthermore, choosing Cu2O NPs as the inner reference could reduce the electrode modification steps. The as-prepared sensor showed good detection performance toward DES in real samples, which provided a new thought for DES reliable detection. Although the ratiometric strategy can effectively reduce the fluctuation of the output signal, some limitations in electrochemical sensor are existed. For example, the fouling of the electrode in the complex determination environment is unavoidable, resulting in the decrease of the electrochemical signal. Therefore, improving the anti-fouling property of the modified electrode is necessary.
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This work was supported by the financial support of the National Natural Science Foundation of China (grant numbers 21775112).
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Xia, Y., Hu, X., Liu, Y. et al. Molecularly imprinted ratiometric electrochemical sensor based on carbon nanotubes/cuprous oxide nanoparticles/titanium carbide MXene composite for diethylstilbestrol detection. Microchim Acta 189, 137 (2022). https://doi.org/10.1007/s00604-022-05249-x
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DOI: https://doi.org/10.1007/s00604-022-05249-x