Graphical abstract
The cavitation effect of high-intensity focused ultrasound could generate the H2O2 and O2–• in situ. Ti3C2-TiO2-AuNPs absorbed and catalyzed H2O2 to produce more O2–•. The synergistic effect leads to a great enhancement of the ECL emission for the air-saturated luminol.
Keywords: Ultrasound-pretreatment, Ti3C2-TiO2-AuNPs, Electrogenerated chemiluminescence, The air-saturated luminol, ROS
Highlights
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High-intensity focused ultrasound triggered the ECL of the air-saturated luminol.
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A novel probe of Ti3C2-TiO2-AuNPs was synthetized.
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The Ti3C2-TiO2-AuNPs could absorb and catalyze the H2O2 to O2–•.
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Through combination of ultrasound and probe, the exosomes were detected sensitively.
Abstract
It is still a great challenge to develop effective strategies to improve the low electrogenerated chemiluminescence (ECL) of air-saturated luminol. Herein, the synergistic effects of Ti3C2-TiO2-AuNPs nano hybrid and high-intensity focused ultrasound pretreatment (ultrasound-pretreatment) were used to significantly improve the ECL emission of the air-saturated luminol, and the mechanism was proposed. The ultrasound-pretreatment as a green method with the cavitation effect could form O2–• and H2O2 in situ as an initiator. TiO2 and Au nanoparticles (AuNPs) were in situ decorated on the Ti3C2 surface to form Ti3C2-TiO2-AuNPs, and it was proved as a highly efficient booster which could catalyze and aggregate H2O2 to the O2–•. The utilization rate of intermediates has been greatly improved. Exosomes as model targets can be sensitively detected by the ECL sensor. The detection limit was 195 particles μL−1. The detection results of exosomes in actual samples are satisfactory. We believe that the ultrasound-pretreatment strategy could be extended to the sensitive detection in the biological sample.
1. Introduction
Luminol is a classic organic ECL emitter, which is favored because of its low oxidation potential, nontoxicity, and so on [1], [2], [3]. In the air-saturated luminol, dissolved oxygen with low toxicity and natural stability is a potential and green endogenous coreactant of luminol [4], [5], [6]. However, the low content and conversion rate of dissolved oxygen result unsatisfied ECL intensity of luminol. To solve the problem, coreactants are usually introduced to activate the air-saturated luminol to generate more the reactive oxygen species (ROS). So far, numerous species, such as, enzymes, nanomaterials (Cu2O@AuNPs, Pt-Au@ZnO and Au-Ag-Pt heteronanostructures [7], [8], [9] and single-atom catalysts [10], [11], [12], [13]) have been developed as the accelerator to promote conversion of O2 to ROS. The developing of green and effective means to boost the ECL strength of the air-saturated luminol is still a hot topic.
It should be noted that ultrasound, as a unique non-invasive means, has played a significant role in biochemical research and clinical treatment [14], [15]. Among them, high-intensity focused ultrasound has the inherent advantages of reducing off target damage and improving ultrasound dept, which is considered to be one of the most promising minimally invasive methods [16], [17]. High negative pressure in the ultrasound focus area can generate cavitation bubbles, then the cavitation bubbles oscillate and collapse. In the process of bubble shrinkage, the internal gas is compressed, resulting in the decomposition of water molecules and O2 to generate ROS, such as O2–•, 1O2, H2O2 and so on [18], [19]. So far, only a few papers on the application of ultrasound in ECL have been reported [20], [21]. Our research group has done the related work in the field of ECL sensing, especially in improving selectivity and sensitivity by using nanomaterials [3], [5]. We speculated that the combination of ultrasound and nanomaterials will be a potential means to boost ECL signal of air-saturated luminol.
Titanium dioxide (TiO2) has become an emerging material in recent years in the biosensing [22], [23], [24], [25]. It was reported that TiO2 could catalyze the oxidation of H2O2 and aggregate ROS, such as O2–• and •OH owing to the band gap dependent catalytic performance of TiO2, which contributes significantly to the ECL emission of luminol [26]. Recently, based on TiO2 nano-hybrid, such as AuAg/TiO2 [27], Att-TiO2 [28], Fe3O4-TiO2@NH2 [29] with strong catalytic performance and good conductivity have attracted much attention in the ECL sensing. However, pre-synthesis of TiO2 usually requires multi-step process and the synthesized TiO2 has a large size, leading to small specific surface area and relatively few active sites of the nano-hybrid. Therefore, it is necessary to find an effective and easy synthesis method of TiO2 with small size to exert its excellent performance in the ECL biosensing. In situ growth of TiO2 on the nanomaterial could be a promising approach. Fortunately, Ti3C2 MXenes as a novel two-dimensional nanomaterial has rich exposed metal sites, excellent reducibility, catalysis and electrical conductivity [30], [31], [32], [33], [34], [35], [36], which can provide rich Ti source to generate the small size of TiO2 in situ. Ti3C2 nanosheets can be used as support platform for TiO2, which can effectively prevent the self-aggregation of TiO2. We expected the Ti3C2-TiO2 generated in situ has an effect of “two birds with one stone” to enhance the ECL response of the air-saturated luminol.
In the present work, we designed a ECL platform with synergistic effect to achieve the goal of sensitive determination of exosomes (Scheme 1). Ultrasound with ultrasonic cavitation effect was a pretreatment means and TiO2 and AuNPs were generated in situ on Ti3C2 to form Ti3C2-TiO2-AuNPs as nanoprobes. The Ti3C2-TiO2-AuNPs nanoprobes can catalyze H2O2 and aggregate ROS generated from ultrasound-pretreatment via cavitation ingeniously to greatly boost the ECL emission of the air-saturated luminol. In the Scheme 1A, the Ti3C2-TiO2-AuNPs nano hybrid was formed by the reducibility of Ti. The Scheme 1B shows the construction of ECL sensor for exosome detection. The CD63 aptamer2 (Apt2) was modified on sodium alginate (SA). Moreover, the Ti3C2-TiO2-AuNPs nano hybrid conjugated with numerous CD63 aptamer1 (Apt1) via Au-S band was captured on the exosomes, and the assembled electrode was detected the exosomes in the luminol pretreated by ultrasound. Scheme 1C shows the illustration for the synergistic effect of ultrasound-pretreatment and Ti3C2-TiO2-AuNPs for the air-saturated luminol. The ultrasound-pretreatment strategy could generate superoxide radical (O2–•) and H2O2 effectively. More importantly, Ti3C2-TiO2-AuNPs nanoprobes not only catalyze H2O2 but also aggregate ROS generated in situ via ultrasound-pretreatment, which can short the diffusion distance and improve the intermediate utilization rate, leading the enhancement of the ECL emission for the air-saturated luminol. The designed ECL biosensor can detect exosomes even in serum, blood, and urine samples, thus proving that it is a promising method for the routine monitoring of exosomes in clinical diagnostics.
Scheme 1.
(A) Synthesis of Ti3C2-TiO2-AuNPs nanoprobes. (B) ECL platform for target detection. (C) The illustration of the synergistic effect of ultrasound-pretreatment and Ti3C2-TiO2-AuNPs for the air-saturated luminol.
2. Experimental
2.1. Materials and reagents
Reagents, materials, instruments, preparation of Ti3C2, Ti3C2-TiO2 and Ti3C2-TiO2-AuNPs are shown in Supplementary Material.
2.2. Exosome extraction and characterization
The culture of MDA-MB-231 cells and the extraction of exosomes refer to our previous work [5]. The TEM image of exosome revealed that the size of approximately is 50 nm [37] (Fig. S1).
2.3. Construction of the ECL platform
The glassy carbon electrode (GCE) with a diameter of 3 mm was polished with 0.3 and 0.05 μm alumina powder by turns and ultrasonic cleaning with ethanol and deionized water respectively. 6 μL of SA solution was modified on the GCE to form SA/GCE. Then, SA/GCE was activated in NHS and EDC (200 mM, 800 mM, v/v = 1:1) at 37°C for 1 h. Then, the SA/GCE was incubated in CD63 Apt2 (1 μM) at 37°C for 2 h to obtain Apt2/SA/GCE. Afterwards, different concentrations of exosomes (100 μL) were incubated on the Apt2/SA/GCE at 37°C for 2 h to form exosomes/Apt2/SA/GCE. The exosomes/Apt2/SA/GCE was incubated in 35 μL Ti3C2-TiO2-AuNPs-Apt1 nanoprobes for 2 h to obtain an ECL biosensor. Finally, the ECL measurement was performed in luminol solution with ultrasound-pretreatment to detect exosomes. In each of the above steps, the electrode needs to be cleaned with ultrapure water and dried with N2 to remove non-specific adsorption.
2.4. Ultrasound -pretreatment and ECL measurement
In this experiment, ultrasound was used as a pretreatment means. The air-saturated luminol solution (50 μM) was pretreated with ultrasound (7.5 W) at 1 MHz for 5 min, and then ultrasound was stopped and removed. Next, the modified electrode (Ti3C2-TiO2-AuNPs-Apt1/exosomes/Apt2/SA/GCE) was used to detect exosomes in the pretreatment luminol solution.
In this work, a three-electrode system was used, the working electrode was the modified electrode, the reference electrode was Ag/AgCl (saturated KCl solution), and the auxiliary electrode was a platinum wire. The scanning potential was set from 0 to 0.6 V, and the scanning speed was 0.1 V s−1. The PMT was 700 V.
3. Results and discussion
3.1. Characterization of the samples
To prove the preparation of Ti3C2-TiO2 and Ti3C2-TiO2-AuNPs, transmission electron microscopy (TEM), high resolution transmission electron microscope (HRTEM), X-ray diffraction (XRD) and X-ray photoelectron spectroscopy (XPS) characterization and EDS analysis were conducted. In the TEM image, the average diameter of Ti3C2 nanosheets was approximately 500 nm with smooth surfaces (Fig. 1A). After oxidation, the layered structure of Ti3C2 was retained and TiO2 particles formed on the Ti3C2 nanosheets in situ can be observed (Fig. 1B and Fig. S2). The Ti3C2-TiO2 was also characterized by XRD (Fig. 1E). The strongest peak of (1 0 4) crystal plane disappeared, the peak of (0 0 2) moved slightly to the left because of expansion of the interlayer of Ti3C2, which indicated that Ti3C2 nanosheets have been successfully synthesized. Meanwhile, the specific diffraction peaks of (1 0 1), (0 0 4), (2 0 0) and (2 1 3) crystal planes of TiO2 appeared and the (0 0 2) peak of Ti3C2 existed, indicating that the Ti3C2-TiO2 was successfully synthesized.
Fig. 1.
The TEM images of Ti3C2 (A), Ti3C2-TiO2 (B) and Ti3C2-TiO2-AuNPs (C). The HRTEM image of Ti3C2-TiO2-AuNPs (D). The XRD analyze of Ti3C2 and Ti3C2 -TiO2 (E).
Moreover, the XPS full spectrum of Ti3C2-TiO2 was shown in Fig. S3A. In the C1s spectra of Ti3C2-TiO2 (Fig. S3B), the peak value (284.7 eV) belonged to adventitious carbon (C-C). The C1s spectra at 281.75 and 285.9 eV correspond to C-Ti and C-O. The wide peak at 455–465 eV, which were related with low valence and high valence Ti species. The peaks at ∼455.4 eV and ∼461.5 eV belonged to Ti-C and Ti-O bonds (Fig. S3C). The formation of Ti3C2-TiO2 nano hybrid could lead to the transition of Ti (II) to Ti (IV). Two typical peaks of O1s of Ti3C2-TiO2 appeared, which were related with Ti-O and C-Ti-Ox (Fig. S3D). The results showed that TiO2 could be in-situ grown on Ti3C2.
The TEM and SEM images of the Ti3C2-TiO2-AuNPs were shown in Fig. 1C and Fig. S4A, indicating that the AuNPs were dispersed on the Ti3C2 nanosheets. Furthermore, Fig. 1D was the HRTEM image of Ti3C2-TiO2-AuNPs, it clearly exhibited the lattice fringe spacings of 0.23 and 0.35 nm, belonged to the (1 0 3) plane of Ti3C2 and the (1 0 1) plane of anatase TiO2. Meanwhile, a clear lattice fringe spacing of about 0.20 nm could be observed, which was consistent with the Au (1 1 1) plane. The characterization of Ti3C2-TiO2-AuNPs by EDS analysis was also proved. Ti and O elements came from Ti3C2 and TiO2, C element came from the Ti3C2. Au element came from the AuNPs (Fig. S4B). In addition, in the UV–vis spectra (Fig. S4C), comparing with curve a, the absorption peak of Ti3C2-TiO2 displayed red shift slightly (curve b). In the curve c, due to the surface plasma absorption of AuNPs, a characteristic absorption peak appeared at 550 nm approximately. The formation of Ti3C2-TiO2-AuNPs was also recorded by the digital photo (Fig. S4D). The Ti3C2-TiO2 was well dispersed in water with dark green (a), the HAuCl4 solution resulted in yellow (b). In contrast, the mixture of Ti3C2-TiO2 and HAuCl4 leaded to purplish red (c), indicating reduction of AuCl4- to form the Ti3C2-TiO2-AuNPs. The EDS mapping of Ti3C2-TiO2-AuNPs was shown in Fig. S5. C, O, Ti, F and Au elements appeared clearly, which could be more directly to demonstrate the successful synthesis of Ti3C2-TiO2-AuNPs.
3.2. The effect of ultrasound-pretreatment and the Ti3C2-TiO2-AuNPs
Firstly, the critical role of Ti3C2-TiO2-AuNPs modified electrode in the air-saturated luminol with ultrasound-pretreatment for 5 min was studied. An ultralow ECL strength was gained on the bare GCE (Fig. 2A, curve a). After modification with Ti3C2, Ti3C2-TiO2 and Ti3C2-AuNPs, Ti3C2-TiO2-AuNPs, the ECL intensity was increased in turn (curve b, c, d and e). These results indicated that the Ti3C2-TiO2-AuNPs nano hybrid showed the best electrocatalytic activity and conductivity than that of Ti3C2, Ti3C2-TiO2 or Ti3C2-AuNPs. Amazingly, aiding by the ultrasound-pretreatment, the Ti3C2-TiO2-AuNPs/GCE in the air-saturated luminol showed the highest ECL signal (curve f), which indicated that the ROS was generated in situ via the unique cavitation effect of ultrasound, which may be an important factor in enhancing ECL emission. In addition, the stability of the Ti3C2-TiO2-AuNPs/GCE with ultrasound-pretreatment was studied under consecutive scanning for 10 cycles. These responses almost remained unchanged, and the RSD was 2.70% (Fig. 2B).
Fig. 2.
(A) ECL-potential curves of (a) bare GCE, (b) Ti3C2/GCE, (c) Ti3C2-TiO2/GCE, (d) Ti3C2-AuNPs/GCE and (e) Ti3C2-TiO2-AuNPs/GCE in luminol. (f) Ti3C2-TiO2-AuNPs/GCE in the air-saturated luminol with ultrasound-pretreatment. (B) The stability of Ti3C2-TiO2-AuNPs/GCE in luminol with ultrasound-pretreatment. (C) ECL signal of the air-saturated luminol with ultrasound-pretreatment under different circumstances. (D) Absorption spectra of TMB* with ultrasound (a) and without ultrasound (b) pretreatment. Error bars are obtained by calculating the standard deviation of 3 parallel experiments.
In addition to the ECL performance, the ECL enhancement mechanism was studied. As shown in the Fig. 2C, the Ti3C2-TiO2-AuNPs/GCE exhibited a strong ECL emission in the air-saturated luminol with ultrasound-pretreatment, a low ECL strength was gained in the luminol which was saturated N2 with ultrasound-pretreatment. These results showed that the dissolved oxygen was important in this system. It is well known that the O2–• was important as the intermediate, and it could oxidize luminol to 3-aminophthalate to generate ECL signal. Therefore, a commercially specific radical scavenger benzoquinone (BQ) for O2–• was introduced to confirm the nature of the involved reactive species. It was seen from the Fig. 2C, the addition of BQ induced 86 % quenching of the ECL signal, which confirmed that O2–• is mainly in the ROS generated by ultrasound-pretreatment and Ti3C2-TiO2-AuNPs.
Since the reactive O2–• could yield H2O2 in the aqueous solution, we tended to confirm the existence of H2O2. The in-situ generation of H2O2 via ultrasound-pretreatment was validated by the H2O2 specific colorimetric method, in which HRP only catalyzed H2O2 to oxidize the substrate TMB to a colored product (TMB*, 650 nm). Compared with curve b in Fig. 2D, a specific absorbance was observed at about 650 nm by ultrasound-pretreatment (curve a), which confirmed the existence of H2O2. Moreover, the maximum absorption peak at 650 nm exhibited a linear fit with the H2O2 concentration (R2 = 0.997) in the range of 10–50 μM (Fig. S6). According to the linear equation of A = -0.018 + 0.034C, the concentration of H2O2 generated by ultrasound-pretreatment was calculated as 26.47 μM.
The high-intensity focused ultrasound with the cavitation effect could form O2–• and H2O2 in situ as an initiator. Ti3C2-TiO2-AuNPs was proved as a highly efficient booster, which could catalyze H2O2 to the O2–•. The synergistic effects of ultrasound-pretreatment and Ti3C2-TiO2-AuNPs greatly improved the ECL intensity in the air-saturated luminol. The ECL mechanism for the application of ultrasound-pretreatment and Ti3C2-TiO2-AuNPs in the air-saturated luminol was proposed in Scheme 1C and Eqs. (1) - (6). A large amount of luminol anions (LH-) were electrochemically oxidized to luminol anionic radicals (L•-) [Eq. (1)]. Dissolved O2 could obtain e- on the electrode to produce O2–• [Eq. (2)]. Ultrasound-pretreatment effectively generated H2O2 and O2–• via cavitation effect [Eq. (3)]. Ti3C2-TiO2-AuNPs could absorb and catalyze the H2O2 to generate more O2–• [Eq. (4)]. Lastly, excited-state intermediate (AP*) was formed via the reaction of L•- with O2–•, which returned to the ground state to obtain excellent ECL emission [Eq. (5), (6)].
| (1) |
| (2) |
| (3) |
| (4) |
| (5) |
| (6) |
3.3. Electrochemical characterizations of the ECL platform
Cyclic voltammetry (CV) was used to characterize the construction of this sensor. After modifying SA on bare electrodes, a smaller current (Fig. 3A, b) than that of the bare GCE (Fig. 3A, a) was shown distinctly. After Apt2 (c) and exosomes (curve d) were incubated, the peak current gradually decreased, because the non-conductive material retarded the electron transfer between the GCE and electroactive material. Finally, when the nanoprobes were connected to the surface of exosomes, the current significantly decreased, owing to the electron transport on electrode surface was blocked by the negatively charged nanoprobes (curve e). The assembly process of this biosensor was also characterized via electrochemical impedance spectroscopy (Fig. 3B). The SA, Apt2, exosomes and Ti3C2-TiO2-AuNPs-Apt1 were modified on the GCE in turn, the arch became bigger gradually, indicating that charge-transfer resistance increased gradually. The above results indicated that the electrode assembly was successful.
Fig. 3.
(A) CV and (B) EIS curves of (a) bare GCE, (b) SA/GCE, (c) Apt2/SA/GCE, (d) exosomes/Apt2/SA/GCE and (e) Ti3C2-TiO2-AuNPs-Apt1/exosomes/Apt2/SA/GCE in [Fe(CN)6]3–/4-.
3.4. Detection of exosomes
Exosomes are vesicles derived from cells (30–200 nm), which carry rich nucleic acids, proteins and lipids for intercellular communication. Because exosomes are highly related to the changes in physiological and pathological conditions for the diseases, especially cancer [38], they are widely considered as potential biomarkers for biological analysis and disease treatment.
The ECL intensity towards different concentrations of exosomes was studied under the optimal experimental conditions (Fig. S7). The ECL response increased with the concentration of exosomes increased from 5.0 × 102 to 1.0 × 105 particles μL−1 with a good linear relationship (Fig. 4A). The linear equation is I = -10411.56 + 4839.51LgC. The limit of detection (LOD) was 195 particles μL−1, which was calculated via formula of LOD=(3σ-b)/k (σ is the background standard deviation, b is the intercept of the linear regression equation, and k is the slope of the linear regression equation), and the squared correlation coefficient (R2) was 0.996. These results showed that this ECL platform had excellent performance for the exosome detection.
Fig. 4.
(A) ECL response of this platform with different concentrations of exosomes (a-f: 5.0 × 102, 1.0 × 103, 5.0 × 103, 1.0 × 104, 5 × 104, 1.0 × 105 particles μL−1, respectively) in the air-saturated luminol with ultrasound-pretreatment. (B) The corresponding linear calibration curve.
3.5. Stability and reproducibility of this platform
Moreover, measuring the ECL responses for 10 cycles was used to prove the stability, the ECL signals did not change significantly (Fig. 5). The reproducibility was evaluated via five Ti3C2-TiO2-AuNPs-Apt1/exosomes/Apt2/SA/GCE, which was prepared by the same modification method. The RSD was 1.50% with 1.0 × 104 particles μL−1 exosomes for the ECL response of five electrodes, showing that this platform had excellent reproducibility.
Fig. 5.
Stability of the ECL sensor in luminol solution with ultrasound-pretreatment for 10 scans. The concentration of exosomes is 1.0 × 104 particles μL−1.
3.6. Sample testing
The feasibility of the constructed sensors to detect target in actual samples is important of clinical diagnosis. Exosomes (1.0 × 103 and 5.0 × 103 particles μL−1) were added into serum, urine and blood samples for recovery experiments, respectively. The recovery rates are between 96.22% and 108.33% with the RSD of 1.67% to 5.51% (Table S1), showing that this biosensor had excellent anti-interference ability in complex matrix and showed potential in clinical sample detection.
4. Conclusion
A novel ECL sensor for detecting exosomes was designed through combining ultrasound-pretreatment with Ti3C2-TiO2-AuNPs nano hybrid. Ultrasound-pretreatment as green and effective means could generate H2O2 and O2–• in situ via ultrasonic cavitation effect. Moreover, Ti3C2-TiO2-AuNPs nano hybrid with strong catalytic performance could catalyze and aggregate ROS to generate more O2–•, thereby enhancing ECL emission of the air-saturated luminol. As a proof of concept, the designed ECL platform was successfully used for exosome detection without additional co-reaction reagent. The LOD was 195 particles μL−1. More importantly, this sensor could be used in detecting exosomes in serum, urine and blood. This green and concise method provides possibilities for the application of the air-saturated luminol.
5. Author statement
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper. Neither the entire article nor any part of its content has been published or has been accepted elsewhere and is not submitted to any other journals.
Declaration of Competing Interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgments
This work was financially supported by the Natural Science Foundation of Shandong Province (ZR2020MB063) and the Taishan Scholar Program of Shandong Province (ts201511027), China.
Footnotes
Supplementary data to this article can be found online at https://doi.org/10.1016/j.ultsonch.2023.106330.
Appendix A. Supplementary data
The following are the Supplementary data to this article:
Data availability
No data was used for the research described in the article.
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