Next Article in Journal
A Self-Assembled G-Quadruplex/Hemin DNAzyme-Driven DNA Walker Strategy for Sensitive and Rapid Detection of Lead Ions Based on Rolling Circle Amplification
Previous Article in Journal
Designing a Graphene Metasurface Organic Material Sensor for Detection of Organic Compounds in Wastewater
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

The Electrochemical Detection of Ochratoxin A in Apple Juice via MnCO3 Nanostructures Incorporated into Carbon Fibers Containing a Molecularly Imprinting Polymer

1
Department of Molecular Biology and Genetic, Faculty of Arts and Sciences, Kafkas University, Kars 36000, Turkey
2
Department of Nutrition and Dietetics, Faculty of Health Sciences, Gaziantep University, Gaziantep 27000, Turkey
3
Department of Biology, Faculty of Arts and Sciences, Kafkas University, Kars 36000, Turkey
4
Department of Chemical Engineering, Faculty of Engineering, Pamukkale University, Denizli 20000, Turkey
5
Department of Nutrition and Dietetics, Faculty of Health Sciences, Hasan Kalyoncu University, Gaziantep 27000, Turkey
*
Author to whom correspondence should be addressed.
Biosensors 2023, 13(8), 760; https://doi.org/10.3390/bios13080760
Submission received: 7 July 2023 / Revised: 24 July 2023 / Accepted: 25 July 2023 / Published: 26 July 2023
(This article belongs to the Section Biosensor Materials)

Abstract

:
A novel electrochemical sensor based on MnCO3 nanostructures incorporated into carbon fibers (MnCO3NS/CF), including a molecularly imprinting polymer (MIP), was developed for the determination of Ochratoxin A (OTA). In this study, a sensitive and selective sensor design for OTA detection was successfully performed by utilizing the selectivity and catalysis properties of MIP and the synthesized MnCO3NS/CF material at the same time. MnCO3 nanostructures incorporated into carbon fibers were first characterized by using various analytical techniques. The sensor revealed a linearity towards OTA in the range of 1.0 × 10−11–1.0 × 10−9 mol L−1 with a detection limit (LOD) of 2.0 × 10−12 mol L−1. The improved electrochemical signal strategy was achieved by high electrical conductivity on the electrode surface, providing fast electron transportation. In particular, the analysis process could be finished in less than 5.0 min without complex and expensive equipment. Lastly, the molecular imprinted electrochemical sensor also revealed superior stability, repeatability and reproducibility.

1. Introduction

The need for food by people is growing parallel with the increasing human population in the world. People may face serious health problems after exposure to mycotoxin contamination due to the storage conditions of large amounts of food or food raw materials produced for mycotoxin growth. Toxic compounds synthesized as a result of the secondary metabolism of mold species are called “mycotoxins”. Mycotoxins are considered to be very significant natural toxins and are one of the important problems that need to be controlled, as they can be found in all areas, can develop in many foods and feed materials and form toxins, and can be transmitted through nutrition, inhalation and skin contact [1]. OTA, which is one of the mycotoxins produced by certain species of Aspergillus and Penicillium genus, is structurally an isocoumarin derivative. OTA is a colorless, crystalline compound, soluble in sodium bicarbonate solutions, recrystallized with weak xylene, with low water solubility and acidic properties. It is a fungal compound that threatens the health of people in every climate due to its greater chemically stable and half-life compared to other derivatives and its immunosuppressant properties that affect organs, such as the liver, kidney and thymus, including carcinogen [2]. OTA can also affect many parts of the human body, such as the central nervous system and protein synthesis. Moreover, OTA inhibits the enzyme by competing with the t-RNA synthetase enzyme, which is responsible for protein synthesis, and causes protein synthesis to stop. According to the results of various experimental studies on animals, the amount of OTA, which the human body can tolerate Daily, is between 0.2 and 4.2 ng kg−1. Different analysis methods have been developed to control the toxic effects of OTA and not exceed both local and global scientific limits. The quality and future of OTA analysis methods in samples also depend on sensitivity, selectivity, time and cost.
In the literature, the chromatography [3], fluorimetric method [4] and surface-enhanced Raman spectroscopy [5] were developed for OTA detection in real samples. Although SERS analysis and fluorescence spectrometry are useful compared to other tests, it is reported that the stability and accuracy of these tests should be further optimized [6]. However, it can be said that analyzes are not carried out with an environmentalist approach since these methods involve excessive chemical consumption. Thus, the need for more effective, environmentally friendly and rapid analysis techniques, which minimize the above-mentioned reasons, still maintains its importance. Electrochemical techniques are the methods in which the electrode-solvent interaction is maximized, and the optimum analysis results are naturally obtained in the fastest way [7,8]. Especially there have been studies in which voltammetric techniques have been used intensively to ensure food safety [9]. Thanks to these techniques, the possible harmful effects of the pesticides, such as mycotoxins, are predicted in advance by making nutrient analyzes instantly and quickly. In conclusion, thanks to the fast signal acquisition capability of voltammetric methods based on aptasensor [10,11,12,13], the analysis of the target molecules, such as pesticides, is performed instantly, thus ensuring safer food consumption.
Transition metal carbonates have started to attract significant attention in the electrochemical applications [14,15]. In particular, MnCO3 nanostructures have been considered as a nanomaterial with high electrochemical application [16,17]. In addition, MnCO3 nanostructures show important advantages containing non-toxicity, simple preparation with high yield and probability of being abundant on earth. In literature, MnCO3@rGO composite was prepared by hydrothermal method and its capacity was obtained as 857 mAh g−1 after a certain scan cycle, providing excellent electrochemical features of MnCO3 nanostructures [18]. Nonetheless, its limited electrical conductivity prevents further electrochemical applications. The formation of MnCO3 nanostructure composites, including carbon fiber, carbon nanotube and graphene oxide, causes the enhancement of electrochemical conductivity and activity. Especially, MnCO3 nanostructures incorporated into carbon fibers may be a better choice in comparison with carbon-based nanomaterials owing to the important application of the MnCO3 nanostructure [17]. Carbon fibers are 4.5 times lighter than steel material and three times more durable, increasing their usage areas. Carbon fibers with a long life are preferred because of their lightness in terms of structure. In addition, it provides a visual advantage as it does not have a problem such as oxidation. They have a lower density than steel, making them a unique material for applications requiring a high weight ratio [19].
MIPs contain active sites that complete the three-dimensional structure of the substrate on the “Key-Lock” model so that the substrate interacts with the active sites that complete its specific structure, just like the key. Molecular imprinting is generally the process of synthesizing polymers with specific recognition sites specific to the template molecule. There are essential components required for the synthesis process: (i) template molecule or molecule to be imprinted, (ii) monomer, (iii) crosslinker, (iv) initiator. After the polymerization process, the analyte molecule is removed from the polymer by washing in order to form spaces in the structure to replace the analyte molecule. The formed cavities recognize the size, structure and chemical properties of the removed analyte molecule and provide binding of the analyte molecule under appropriate conditions [20,21]. In the following processes, when a solution containing the analyte molecule is applied to the imprinted polymer, it will recognize the analyte molecule thanks to its active recognition sites, and, thus, the analyte molecule will be re-attached to the polymer [22]. To prepare a molecularly imprinted polymer, two different approaches are used, covalent and non-covalent, depending on the interaction between the functional monomer and the template molecule [22,23]. In covalent imprinting, covalent bonding occurs first between the functional monomer and the template molecule. In order to form MIPs after polymerization, the covalent bonds formed are broken and removed from the polymer [24]. In this imprinting, functional monomers, which can interact non-covalently with the template molecule, are used. The interaction between the functional monomer and the template molecule occurs through non-covalent interactions, such as hydrogen bonding and van der Waals interactions. When the polymerization is completed, the template molecule is removed from the polymer with the help of the solvent [25]. Pyrrole monomer is one of the most widely used conductive polymers in MIPs-based electrochemical sensor applications because of its high conductivity, high stability in a wide range of pH, electropolymerization efficiency and physical/chemical inertness [26,27].
There are some MIP-based analytical methods developed for OTA analysis in the literature. For instance, MIP-based magnetic photonic crystal microspheres for OTA analysis were prepared, and a linear detection range of 5–20,000 ng mL−1 and a LOD of 0.675 ng mL−1 were obtained with a good recovery [28]. In addition, the chromatographic detection based on microfiber graphene/nanofibers, including MIP, was completed for OTA determination in milk beverages and a linear detection range of 0.2–40.0 µg L−1 was determined with good repeatability [29]. In another study, OTA imprinted nanoMIPs were developed by using a solid-phase polymerization technique, including phenylalanine derivative as a monomer. The results showed that the high selectivity was accomplished [30]. In another study, a MIP-assisted sample clean-up method was developed to remove OTA from wine samples. This method was based on a two-dimensional solid-phase extraction on C18-silica, and the developed method showed a LOD of 0.01 ng mL−1 [31]. The oligo(ethylene glycol) monomethyl ether methacrylate-based MIPs was also synthesized by atom transfer radical polymerization for OTA removal, and the values of recovery were obtained as 97.1–97.4% [32]. Finally, a ratiometric electrochemical sensor based on magnetic MIP was presented with high reproducibility and a linear detection range of 0.5–15.0 µmol L−1 and a LOD of 14.0 nmol L−1 was obtained [33].
This paper provides a rapid and selective OTA detection method via a molecularly imprinted sensor based on MnCO3 nanostructures incorporated into carbon fibers. Thanks to the high electrical conductivity caused by MnCO3 nanostructures incorporated into carbon fibers on the electrode surface, a sensitive OTA analysis was performed with high selectivity. Hence, a seminal study has been presented to the world of literature in terms of safer food consumption by developing a novel OTA imprinted sensor.

2. Experimental

2.1. Chemicals and Apparatus

OTA, ochratoxin B (OTB), aflatoxin B1 (AFB1), aflatoxin B2 (AFB2), citrinin (CIT), catechol (CAT), resveratrol (RES), KMnO4 and pyrrole (Py) monomer were maintained by Sigma-Aldrich. Phosphate-buffered saline (0.1 mol L−1, pH 7.0, PBS) of supporting electrolytes was utilized for electrochemical measurements.
ZEISS EVO 50 SEM (Tokyo, Japan), JEOL 2100 TEM (Tokyo, Japan), a Rikagu Miniflex X-ray diffractometer using mono-chromatic CuKα (new 6th-generation general purpose benchtop system, Tokyo, Japan) and a PHI 5000 Versa Probe type X-ray photoelectron spectrometer (Tokyo, Japan) techniques were applied for the determination of structural analysis of MnCO3NS and MnCO3NS/CF composite. Gamry Reference 600 workstation (Warminster, PA, USA) was also performed for the electrochemical investigations by using DPV, EIS, and CV.

2.2. Production of MnCO3NS and MnCO3NS/CF Composite

The hydrothermal technique was utilized for the preparation of the MnCO3NS/CF composite. The commercial carbon fiber cloth (pyrolytically stripped, platelets(conical), >98% carbon basis) was used as a source for the carbon fibers and maintained by Sigma-Aldrich. Before MnCO3 growth, the commercial carbon fiber (CF) cloth interacted with 50:50 (v/v) ethanol and acetonitrile solution under strong sonication for 20 min. Then, CF was activated in concentrated HNO3 (50.0%) for 45 min. After that, the solution of KMnO4 (50.0 mmol L−1) and starch (2.0 g) in ultra-pure water (50.0 mL) was prepared, and this solution was subjected to stirring treatment for 45 min. Then, the solution and CF piece (3.0 cm × 3.0 cm) were transferred to a Teflon-lined hydrothermal autoclave (Techinstro Industries, Maharashtra, India) and subjected to the heating treatment at 180 °C for 10 h. The product MnCO3NS/CF composite was washed with ultra-pure water two times and dried at 100 °C. In addition, MnCO3NS was prepared by the same procedure without CF [17].

2.3. Production of MnCO3NS/CF Modified Glassy Carbon Electrode (MnCO3NS/CF/GCE)

The procedure of surface cleaning of GCE electrodes was performed according to our previous paper [34]. The GCE was modified with MnCO3NS/CF composite solution (40.0 μL, 0.5 mg mL−1) and an IR lamp was utilized to remove the solvent for 20 min, providing MnCO3NS/CF/GCE. MnCO3NS-modified GCE surfaces (MnCO3NS/GCE) were formed by the method described above.

2.4. OTA Imprinted Sensor and OTA Removal

Firstly, 25.0 mmol L−1 OTA solution, including 100.0 mmol L−1 Py was prepared into the cell for the development of OTA imprinted polymer on MnCO3NS/CF/GCE. Then, 20 continuous cycles were scanned on MnCO3NS/CF/GCE in +0.00/+1.00 V range, and the current responses at +0.70 V were constantly followed to produce OTA imprinted MnCO3NS/CF/GCE (MIP/MnCO3NS/CF/GCE) (Scheme 1) [35]. Then, the template molecule (OTA) was removed by using NaCl solution (10.0 mL, 1.0 mol L−1). The described method was utilized for the development of OTA non-imprinted MnCO3NS/CF/GCE (NIP/MnCO3NS/CF/GCE) to indicate the imprinting selectivity.

2.5. Sample Preparation

Apple juice samples taken from the local supermarket were first kept in the refrigerator at +4 °C for 1 day and then transferred to a test tube. After adding ethanol (5.0 mL) to this test tube, it was exposed to a shake bath system for 15 min. After the centrifugation for 5 min at 1000 rpm, the upper phase was spiked with a fine syringe [36]. Then, the upper phase was diluted with 0.1 M PBS (3.0 mL, pH 7.0) and transported into the electrochemical cell for OTA analysis. MIP/MnCO3NS/CF/GCE, platinum wire and Ag/AgCl/KCl(sat) were used for the working electrode, counter electrode and reference electrode, respectively, for the analysis. Analytical applications were carried out from the calibration graph obtained by plotting the current values of the peaks occurring at +0.5 V in the +0.2/+1.0 V potential range against the OTA concentration.

3. Results and Discussion

3.1. Characterizations of MnCO3NS/CF

After the ultrasonication treatment of commercial CF in HNO3 (50%) for 45 min, MnCO3NS was interconnected onto the CF surface by hydrothermal process. The surface characterizations of CF and MnCO3NS were explored by SEM (Figure S1). According to Figure S1A, the diameter of the smooth carbon fiber was calculated as about 7–8 µm, and the diameter of pure MnCO3NS was obtained as about 3–4 µm (Figure S1B). After the preparation of MnCO3NS interconnected onto the CF surface by hydrothermal method, the granular CF formation occurred via MnCO3NS interconnection (Figure 1A,B). According to Figure 1, the diameter of MnCO3NS/CF was calculated to be about 9–10 µm, indicating the successful preparation of MnCO3NS on the CF surface, including interconnected interaction.
TEM measurements were performed for the determination of the elemental composition of MnCO3NS (Figure S2). According to Figure S2A, the size of MnCO3NS was obtained as about 50–51 nm. This result was confirmed in harmony with SEM measurements. In addition, unclear crystalline fringes (Figure S2B) verified the non-crystallization of MnCO3NS. The presence of C, Mn, and O elements was verified on the EDX image (Figure S2C), providing the successful preparation of MnCO3NS/CF nanocomposite and the specific surface area of MnCO3NS/CF nanocomposite, including interconnected interaction. This specific surface area also indicated efficient contact with electrolyte solution and suggested the superior electrochemical activity [17].
The crystal structures of MnCO3NS and MnCO3NS/CF composite were investigated by XRD (Figure 2A). Six obvious XRD peaks at 24.08°, 31.79°, 37.79°, 41.93°, 45.07° and 51.36° corresponded to (012), (104), (110), (113), and (204) planes, respectively. XRD peak at 24.08° was attributed to the carbon phase, and there were no impurity peaks, indicating that the successful preparations of MnCO3NS and MnCO3NS/CF composite were performed in this work. In addition, Raman spectra (Figure 2B) were recorded for the structural investigation of MnCO3NS and MnCO3NS/CF composite. Three obvious Raman peaks at 320 cm−1, 373 cm−1 and 660 cm−1 were attributed to the specific peaks of MnCO3NS. The Raman peaks at 320 cm−1 and 373 cm−1 corresponded to the translational and librational modes. The peak at 660 cm−1 also corresponded to the in-plane bend mode [15]. Finally, two Raman peaks at 1392 cm−1 and 1591 cm−1 were attributed to the D band and G band of CF. Thus, XRD and the Raman results confirmed the successful preparation of MnCO3NS on the CF surface.
Mn2p, O1s and C1s high-resolution XPS spectrums of MnCO3NS/CF composite were given in Figure 3. According to the survey spectrum of Figure 3A, the presence of manganese, oxygen and carbon elements verified MnCO3NS/CF composite. The XPS peaks at 653.08 eV and 640.39 eV on Mn2p spectra (Figure 3B) were attributed to Mn2p1/2 and Mn2p3/2, respectively [37]. In addition, three XPS peaks at 532.71 eV, 531.09 eV and 530.46 eV corresponded to O-Mn, CO32− and C-O bonds, respectively (Figure 3C). On the C1s spectrum (Figure 3D), three XPS peaks at 286.13 eV, 284.69 eV and 283.94 eV corresponded to C-O, C-C and C-Mn, respectively. It was concluded that the C-Mn bond resulted from the interaction between MnCO3 and CF. Hence, MnCO3NS was bridged to CF via C-Mn bonds, providing chemical stability during the electrochemical sensor application [38,39].

3.2. Electrochemical Characterizations of MnCO3NS and MnCO3NS/CF Composite Modified Electrodes

CV and EIS measurements were obtained to demonstrate the electrochemical performances of MnCO3NS/GCE and MnCO3NS/CF/GCE in 5.0 mmol L−1 [Fe(CN)6]3−/4− (Figure 4). Electrochemical current signals at +0.400 and +0.200 V appeared at bare GCE (curve a of Figure 4A). However, the more prominent electrochemical performances were obtained at MnCO3NS/GCE (curve b of Figure 4A) due to the large battery capacity of the MnCO3NS [16,40]. After the preparation of MnCO3NS interconnected onto the CF surface, the more easy electron transfer occurred on MnCO3NS/CF/GCE, and the obvious electrochemical signals were observed in comparison with MnCO3NS/GCE (curve c of Figure 4A) [17]. If we want to examine the electrochemical oxidation process, the oxidation of the OTA molecule occurred based on a mechanism involving 2 protons and 2 electrons through the amine group (Scheme 1) [41]. The number of the transferred electrons was calculated by using Laviron’s Equation (1) (See Supplementary Data for the explanations of terms):
Ep = E0 + [RT/(1 − α)nF] Inν
In addition, when CV anodic peak currents were plotted against the square root of the scan rate (10–1000 mV s−1) (R2 = 0.9991), the obtained linearity indicated that the oxidation phenomenon was diffusion-controlled [42].
EIS measurements were applied to confirm the CV results (Figure 4B). Experimental data fitting to the Randles circuit for MnCO3NS/CF/GCE were shown on the inset of Figure 4B, including the charge transfer resistance (Rct), the solution resistance (Rs) and the constant phase element (CPE). Rct values were studied to be 45 ohm for bare GCE, 35 ohm for MnCO3NS/GCE, and 25 ohm for MnCO3NS/CF/GCE, confirming the accuracy of CV results.

3.3. Fabrication of OTA Imprinted Polymer on MnCO3NS/CF/GCE

According to the increase in the number of scans, the permanent decrease in electrochemical signals proved that OTA imprinted polymers were formed on MnCO3NS/CF/GCE (Figure 5A). Electrochemical measurements were made using MIP and NIP electrodes in the presence of 0.5 nmol L−1 OTA and without OTA to show that molecularly imprinted polymers bring a high selectivity to the target molecule. As expected, no current signals were observed on MIP/MnCO3NS/CF/GCE in the presence of pH 7.0, PBS solution (Curve a of Figure 5B). In comparison with MIP (curve c of Figure 5B) and NIP (curve b of Figure 5B) electrodes, it was seen that OTA imprinted molecularly imprinted polymers provided a more selective sensor affinity towards OTA molecules. In addition, three OTA imprinted electrochemical electrodes were prepared and applied to 0.5 nmol L−1 OTA in the presence of pH 7.0, PBS solution (Figure 5C). These results, which were in agreement with Figure 5B, prove that the MIP/MnCO3NS/CF/GCE electrode can be used for future studies.

3.4. Optimization Studies

3.4.1. pH Effect

The pH of the working environment is the most important parameter affecting the signal strength of the working electrode in electrochemical sensor studies. When Figure 6A was examined, while the working electrode produced maximum signal up to pH 7.0, these signals decreased after pH 7.0. Thus, 7.0 was chosen as the ideal pH.

3.4.2. Mole Ratio OTA to Py Monomer Effect

In molecularly imprinted electrochemical sensor studies, the stoichiometric ratio between the analyte and the monomer significantly affects the sensitivity of the method. When the monomer ratio is low, the number of binding sites on the electrode surface is low. Thus, 100.0 mmol L−1 Py and 25.0 mmol L−1 OTA were used as monomer and target molecules (Figure 6B).

3.4.3. Desorption Time Effect

Complete removal of the analyte molecule from the electrode surface is an important factor in fast electrochemical sensor designs. In this study, several desorption times were tried, and it was seen that the analyte molecules were completely removed from the electrode surface at the end of the 20th min (Figure 6C).

3.4.4. Scan Cycle Effect

In electrochemistry-based polymerization techniques, the surface thickness of the working electrode is another significant factor affecting the performance of the sensor. The number of scans must be kept at an optimal level so that non-specific interactions caused by the thick monomer layer on the surface of the working electrode do not occur. We observed that working electrodes with 20 scan numbers produced the highest sensor response when working electrodes prepared with different scan numbers were used (Figure 6D).

3.5. Quantification Limit (LOQ) and LOD Values

The linearity range of MIP/MnCO3NS/CF/GCE was first formed by using OTA concentration and DPV signals. Thus, y (µA) = 9.8744x (COTA, nmol L−1) − 0.0246, (R2 = 0.9989) was given in Figure 7 and LOQ, and LOD values were computed as 1.0 × 10−11 mol L−1, and 2.0 × 10−12 mol L−1, respectively (See Supplementary Data for the equations). In addition, Table 1 indicates the sensitivity features of MIP/MnCO3NS/CF/GCE in comparison with the existing methods for OTA detection. Thus, we presented a more sensitive detection method for OTA in comparison with the reported methods. Since we produced MnCO3NS/CF composite by using a hydrothermal process, we developed an environmentally friendly analytical process for OTA detection and zero waste generation occurred during sensor preparation. Due to the high stability, selectivity, repeatability and reproducibility, the OTA imprinted sensor is also utilized as a reference technique for mycotoxin detection. Lastly, we believe that this OTA imprinted sensor will be a pioneer for healthier food consumption.

3.6. Recovery Assessment

Recovery experiments were performed in apple juice. According to Table 2, the values close to 100% verified a high recovery of MIP/MnCO3NS/CF/GCE.

3.7. Selectivity, Stability, Repeatability and Reproducibility Performances of MIP/MnCO3NS/CF/GCE

For selectivity experiments of MIP/MnCO3NS/CF/GCE, 6 chemical agents with similar chemical features were detected (OTB, AFB1, AFB2, CIT, CAT and RES). The electrochemical signals (µA) were obtained for 1.0 nmol L−1 OTA, 100.0 nmol L−1 OTB, 100.0 nmol L−1 AFB1, 100.0 nmol L−1 AFB2, 100.0 nmol L−1 CIT, 100.0 nmol L−1 CAT and 100.0 nmol L−1 RES on MIP/MnCO3NS/CF/GCE and NIP/MnCO3NS/CF/GCE (Figure S3A,B). These electrochemical signals are given in Table 3, including selectivity coefficient (k) and relative selectivity coefficient (k′) values. It was concluded that MIP/MnCO3NS/CF/GCE was 7.92, 9.50, 12.67, 19.00, 31.67 and 47.50 times more selective for OTA than OTB, AFB1, AFB2, CIT, CAT and RES, respectively, owing to specific nano-cavities of OTA.
The stability test of the OTA imprinted sensor was evaluated for 7 weeks (Figure S4). The observed current response in the seventh week was ~97.19% of the current response in the first week, indicating the high stability of the OTA imprinted electrode.
The relative standard deviation (RSD) value was obtained as 0.19% for 45 consecutive measurements. Hence, the high repeatability of one MIP/MnCO3NS/CF/GCE electrode was confirmed.
Finally, the reproducibility test of 20 different OTA imprinted sensors was investigated, and 20 different OTA imprinted sensors were applied to 0.5 nmol L−1 OTA. RSD of 0.77% was obtained for 20 different measurements, providing a high reproducibility.

4. Conclusions

In this study, a sensitive and selective molecularly imprinted electrochemical sensor based on MnCO3NS/CF was presented for OTA detection. MnCO3NS/CF composite improved the electrochemical performances in OTA analysis. This result can be explained by using these reasons: (i) MnCO3NS, including interconnected structures, provided high electrical conductivity during the electrochemical process, ensuring rapid electron transportation. (ii) MnCO3NS was incorporated into the CF surface through Mn-C bonds, providing electrode stability. According to analytical data, the OTA imprinted electrode indicated linearity (1.0 × 10−11–1.0 × 10−9 mol L−1) with a low LOD of 2.0 × 10−12 mol L−1, ensuring excellent sensitivity and selectivity. The fact that the developed sensor also has an environmentally friendly feature will lead to the emergence of new perspectives for the detection and analysis of other mycotoxins in the future. In addition, OTA imprinted electrode’s ability to make rapid analysis in a short time can cause more reliable food consumption.

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/bios13080760/s1, Figure S1: SEM images of (A) CF and (B) MnCO3NS; Figure S2: (A) TEM image of MnCO3NS, (B) HRTEM image of MnCO3NS and (C) EDX spectrum of MnCO3NS/CF composite; Figure S3: DPVs of (A) MIP/MnCO3NS/CF/GCE and (B) NIP/MnCO3NS/CF/GCE in 1.0 nmol L−1 OTA, 100.0 nmol L−1 OTB, 100.0 nmol L−1 AFB1, 100.0 nmol L−1 AFB2, 100.0 nmol L−1 CIT, 100.0 nmol L−1 CAT and 100.0 nmol L−1 RES; Figure S4: Stability test of MIP/MnCO3NS/CF/GCE including 0.5 nmol L−1 OTA (n = 6).

Author Contributions

Conceptualization, Methodology, Writing—review & editing: M.M.K. and H.A.D.; Writing—original draft, Visualization, Investigation: İ.K. and N.A.; Supervision, Conceptualization, Funding acquisition: M.L.Y. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the Turkish Academy of Sciences (TUBA-GEBIP).

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

The original data in this study are included in this study, and further inquiries can be directed to the corresponding author.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Richard, J.L. Some major mycotoxins and their mycotoxicoses—An overview. Int. J. Food Microbiol. 2007, 119, 3–10. [Google Scholar] [CrossRef] [PubMed]
  2. Al-Anati, L.; Petzinger, E. Immunotoxic activity of ochratoxin A. J. Vet. Pharmacol. Ther. 2006, 29, 79–90. [Google Scholar] [CrossRef] [PubMed]
  3. Li, X.J.; Ma, W.; Ma, Z.Y.; Zhang, Q.H.; Li, H.M. Recent progress in determination of ochratoxin a in foods by chromatographic and mass spectrometry methods. Crit. Rev. Food Sci. Nutr. 2022, 62, 5444–5461. [Google Scholar] [CrossRef] [PubMed]
  4. Wu, G.; Xiong, Z.W.; Oh, S.H.; Ren, Y.R.; Wang, Q.; Yang, L.Z. Two-color, ultra-sensitive fluorescent strategy for Ochratoxin A detection based on hybridization chain reaction and DNA tweezers. Food Chem. 2021, 356, 129663. [Google Scholar] [CrossRef] [PubMed]
  5. Song, L.C.; Li, J.L.; Li, H.; Chang, Y.W.; Dai, S.J.; Xu, R.M.; Dou, M.H.; Li, Q.J.; Lv, G.P.; Zheng, T.S. Highly sensitive SERS detection for Aflatoxin B1 and Ochratoxin A based on aptamer-functionalized photonic crystal microsphere array. Sens. Actuators B-Chem. 2022, 364, 131778. [Google Scholar] [CrossRef]
  6. Wang, H.; Zhao, B.B.; Ye, Y.F.; Qi, X.Y.; Zhang, Y.T.; Xia, X.L.; Wang, X.L.; Zhou, N.D. A fluorescence and surface-enhanced Raman scattering dual-mode aptasensor for rapid and sensitive detection of ochratoxin A. Biosens. Bioelectron. 2022, 207, 114164. [Google Scholar] [CrossRef]
  7. Gupta, B.; Perillo, M.L.; Siegenthaler, J.R.; Christensen, I.E.; Welch, M.P.; Rechenberg, R.; Banna, G.M.H.U.; Galstyan, D.; Becker, M.F.; Li, W.; et al. In Vitro Biofouling Performance of Boron-Doped Diamond Microelectrodes for Serotonin Detection Using Fast-Scan Cyclic Voltammetry. Biosensors 2023, 13, 576. [Google Scholar] [CrossRef]
  8. Erdem, A.; Eksin, E. Zip Nucleic Acid-Based Genomagnetic Assay for Electrochemical Detection of microRNA-34a. Biosensors 2023, 13, 144. [Google Scholar] [CrossRef]
  9. Zhong, W.; Zou, J.; Yu, Q.; Gao, Y.; Qu, F.; Liu, S.; Zhou, H.; Lu, L. Ultrasensitive indirect electrochemical sensing of thiabendazole in fruit and water by the anodic stripping voltammetry of Cu2+ with hierarchical Ti3C2Tx-TiO2 for signal amplification. Food Chem. 2023, 402, 134379. [Google Scholar] [CrossRef]
  10. Zhang, T.; Xu, S.; Lin, X.; Liu, J.; Wang, K. Label-Free Electrochemical Aptasensor Based on the Vertically-Aligned Mesoporous Silica Films for Determination of Aflatoxin B1. Biosensors 2023, 13, 661. [Google Scholar] [CrossRef]
  11. Zhang, T.; Yang, L.; Yan, F.; Wang, K. Vertically-Ordered Mesoporous Silica Film Based Electrochemical Aptasensor for Highly Sensitive Detection of Alpha-Fetoprotein in Human Serum. Biosensors 2023, 13, 628. [Google Scholar] [CrossRef]
  12. Yuan, R.; Fu, Z.; He, Y.; Deng, Y.; Xi, J.; Xing, X.; He, H. Size-controlling preparation of covalent organic framework nanospheres for electrochemical impedimetric aptasensing of oxytetracycline. Talanta 2023, 265, 124834. [Google Scholar] [CrossRef] [PubMed]
  13. Zhang, H.-W.; Zhu, Q.-Q.; Yuan, R.; He, H. Crystal engineering of MOF@COF core-shell composites for ultra-sensitively electrochemical detection. Sens. Actuators B Chem. 2021, 329, 129144. [Google Scholar] [CrossRef]
  14. Bhojane, P.; Sinha, L.; Goutam, U.K.; Shirage, P.M. A 3D mesoporous flowers of nickel carbonate hydroxide hydrate for high-performance electrochemical energy storage application. Electrochim. Acta 2019, 296, 112–119. [Google Scholar] [CrossRef]
  15. Zhou, L.; Kong, X.; Gao, M.; Lian, F.; Li, B.; Zhou, Z.; Cao, H. Hydrothermal Fabrication of MnCO3@rGO Composite as an Anode Material for High-Performance Lithium Ion Batteries. Inorg. Chem. 2014, 53, 9228–9234. [Google Scholar] [CrossRef]
  16. Ruan, S.J.; Ma, C.; Wang, J.T.; Qiao, W.M.; Ling, L.C. Facile synthesis of graphene-wrapped porous MnCO3 microspheres with enhanced surface capacitive effects for superior lithium storage. Chem. Eng. J. 2019, 367, 64–75. [Google Scholar] [CrossRef]
  17. Suo, G.; Cheng, Y.; Zhang, J.; Ahmed, S.M.; Hou, X.; Yang, Y.; Ye, X.; Zhang, L. Interconnected MnCO3 nanostructures anchored on carbon fibers with enhanced potassium storage performance. Mater. Today Chem. 2022, 25, 100904. [Google Scholar] [CrossRef]
  18. Udayabhanu, G.; Muralikrishna, S.; Kishore, B.; Nagabhushana, H.; Suresh, D.; Sharma, S.C.; Nagaraju, G. One pot green synthesis of MnCO3–rGO composite hybrid superstructure: Application to lithium ion battery and biosensor. New J. Chem. 2017, 41, 12854–12865. [Google Scholar] [CrossRef]
  19. Forintos, N.; Czigany, T. Multifunctional application of carbon fiber reinforced polymer composites: Electrical properties of the reinforcing carbon fibers—A short review. Compos. Part B Eng. 2019, 162, 331–343. [Google Scholar] [CrossRef]
  20. Wu, Y.; Deng, P.; Tian, Y.; Ding, Z.; Li, G.; Liu, J.; Zuberi, Z.; He, Q. Rapid recognition and determination of tryptophan by carbon nanotubes and molecularly imprinted polymer-modified glassy carbon electrode. Bioelectrochemistry 2020, 131, 107393. [Google Scholar] [CrossRef] [PubMed]
  21. Wu, Y.; Li, G.; Tian, Y.; Feng, J.; Xiao, J.; Liu, J.; Liu, X.; He, Q. Electropolymerization of molecularly imprinted polypyrrole film on multiwalled carbon nanotube surface for highly selective and stable determination of carcinogenic amaranth. J. Electroanal. Chem. 2021, 895, 115494. [Google Scholar] [CrossRef]
  22. BelBruno, J.J. Molecularly Imprinted Polymers. Chem. Rev. 2019, 119, 94–119. [Google Scholar] [CrossRef] [PubMed]
  23. Vasapollo, G.; Sole, R.D.; Mergola, L.; Lazzoi, M.R.; Scardino, A.; Scorrano, S.; Mele, G. Molecularly Imprinted Polymers: Present and Future Prospective. Int. J. Mol. Sci. 2011, 12, 5908–5945. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  24. Cormack, P.A.G.; Elorza, A.Z. Molecularly imprinted polymers: Synthesis and characterisation. J. Chromatogr. B 2004, 804, 173–182. [Google Scholar] [CrossRef]
  25. Yan, H.; Row, K.H. Characteristic and Synthetic Approach of Molecularly Imprinted Polymer. Int. J. Mol. Sci. 2006, 7, 155–178. [Google Scholar] [CrossRef] [Green Version]
  26. Lu, B.; Xia, J.; Wang, Z.; Zhang, F.; Yang, M.; Li, Y.; Xia, Y. Molecularly imprinted electrochemical sensor based on an electrode modified with an imprinted pyrrole film immobilized on a β-cyclodextrin/gold nanoparticles/graphene layer. RSC Adv. 2015, 5, 82930–82935. [Google Scholar] [CrossRef]
  27. Chen, H.-J.; Zhang, Z.-H.; Cai, R.; Chen, X.; Liu, Y.-N.; Rao, W.; Yao, S.-Z. Molecularly imprinted electrochemical sensor based on amine group modified graphene covalently linked electrode for 4-nonylphenol detection. Talanta 2013, 115, 222–227. [Google Scholar] [CrossRef]
  28. Dou, M.; Wang, S.; Li, W.; Li, Q.; Xu, J.; Li, J. High-performance molecularly imprinted polymers grafted magnetic photonic crystal microspheres for selective enrichment of ochratoxin a. J. Chromatogr. A 2023, 1695, 463932. [Google Scholar] [CrossRef]
  29. Kholová, A.; Lhotská, I.; Erben, J.; Chvojka, J.; Švec, F.; Solich, P.; Šatínský, D. Comparison of nanofibers, microfibers, nano/microfiber graphene doped composites, molecularly imprinted polymers, and restricted access materials for on-line extraction and chromatographic determination of citrinin, zearalenone, and ochratoxin A in plant-based milk beverages. Microchem. J. 2023, 191, 108937. [Google Scholar] [CrossRef]
  30. Serra, T.; Anfossi, L.; Cavalera, S.; Chiarello, M.; Nardo, F.D.; Testa, V.; Baggiani, C. Ochratoxin A-Imprinted nanoMIPs Prepared by Solid Phase Synthesis: Effect of Mimic Template on Binding Properties. Macromol 2023, 3, 234–244. [Google Scholar] [CrossRef]
  31. Maier, N.M.; Buttinger, G.; Welhartizki, S.; Gavioli, E.; Lindner, W. Molecularly imprinted polymer-assisted sample clean-up of ochratoxin A from red wine: Merits and limitations. J. Chromatogr. B 2004, 804, 103–111. [Google Scholar] [CrossRef] [PubMed]
  32. Turan, E.; Şahin, F. Molecularly imprinted biocompatible magnetic nanoparticles for specific recognition of Ochratoxin A. Sens. Actuators B Chem. 2016, 227, 668–676. [Google Scholar] [CrossRef]
  33. Hu, X.; Xia, Y.; Liu, Y.; Chen, Y.; Zeng, B. An effective ratiometric electrochemical sensor for highly selective and reproducible detection of ochratoxin A: Use of magnetic field improved molecularly imprinted polymer. Sens. Actuators B Chem. 2022, 359, 131582. [Google Scholar] [CrossRef]
  34. Yola, M.L.; Atar, N.; Qureshi, M.S.; Ustundag, Z.; Solak, A.O. Electrochemically grafted etodolac film on glassy carbon for Pb(II) determination. Sens. Actuators B-Chem. 2012, 171, 1207–1215. [Google Scholar] [CrossRef]
  35. Yola, M.L. Carbendazim imprinted electrochemical sensor based on CdMoO4/g-C3N4 nanocomposite: Application to fruit juice samples. Chemosphere 2022, 301, 134766. [Google Scholar] [CrossRef] [PubMed]
  36. Yola, M.L.; Gupta, V.K.; Atar, N. New molecular imprinted voltammetric sensor for determination of ochratoxin A. Mater. Sci. Eng. C-Mater. Biol. Appl. 2016, 61, 368–375. [Google Scholar] [CrossRef]
  37. Xiao, L.; Wang, S.Y.; Wang, Y.F.; Meng, W.; Deng, B.H.; Qu, D.Y.; Xie, Z.Z.; Liu, J.P. High-Capacity and Self-Stabilized Manganese Carbonate Microspheres as Anode Material for Lithium-Ion Batteries. ACS Appl. Mater. Interfaces 2016, 8, 25369–25378. [Google Scholar] [CrossRef]
  38. Suo, G.Q.; Zhang, J.Q.; Li, D.; Yu, Q.Y.; Wan, W.A.; He, M.; Feng, L.; Hou, X.J.; Yang, Y.L.; Ye, X.H.; et al. N-doped carbon/ultrathin 2D metallic cobalt selenide core/sheath flexible framework bridged by chemical bonds for high-performance potassium storage. Chem. Eng. J. 2020, 388, 124396. [Google Scholar] [CrossRef]
  39. Chong, S.K.; Sun, L.; Shu, C.Y.; Guo, S.W.; Liu, Y.N.; Wang, W.; Liu, H.K. Chemical bonding boosts nano-rose-like MoS2 anchored on reduced graphene oxide for superior potassium-ion storage. Nano Energy 2019, 63, 103868. [Google Scholar] [CrossRef]
  40. Li, Q.; Liu, Z.W.; Wang, C.; Zhao, Y.H.; Che, R.C. Doping of Ni and Zn Elements in MnCO3: High-Power Anode Material for Lithium-Ion Batteries. Small 2018, 14, 1702574. [Google Scholar] [CrossRef]
  41. Yao, Y.; Wen, Y.; Zhang, L.; Wang, Z.; Zhang, H.; Xu, J. Electrochemical recognition and trace-level detection of bactericide carbendazim using carboxylic group functionalized poly(3,4-ethylenedioxythiophene) mimic electrode. Anal. Chim. Acta 2014, 831, 38–49. [Google Scholar] [CrossRef]
  42. Arteshi, Y.; Lima, D.; Tittlemier, S.A.; Kuss, S. Rapid and inexpensive voltammetric detection of ochratoxin A in wheat matrices. Bioelectrochemistry 2023, 152, 108451. [Google Scholar] [CrossRef] [PubMed]
  43. Yang, C.; Abbas, F.; Rhouati, A.; Sun, Y.Y.; Chu, X.L.; Cui, S.N.; Sun, B.B.; Xue, C.Y. Design of a Quencher-Free Fluorescent Aptasensor for Ochratoxin A Detection in Red Wine Based on the Guanine-Quenching Ability. Biosensors 2022, 12, 297. [Google Scholar] [CrossRef] [PubMed]
  44. Wang, H.; Chen, L.; Li, M.; She, Y.X.; Zhu, C.; Yan, M.M. An Alkyne-Mediated SERS Aptasensor for Anti-Interference Ochratoxin A Detection in Real Samples. Foods 2022, 11, 3407. [Google Scholar] [CrossRef] [PubMed]
  45. Zhao, Y.Y.; Liu, R.J.; Sun, W.Y.; Lv, L.; Guo, Z.J. Ochratoxin A detection platform based on signal amplification by Exonuclease III and fluorescence quenching by gold nanoparticles. Sens. Actuators B Chem. 2018, 255, 1640–1645. [Google Scholar] [CrossRef]
  46. He, Y.; Tian, F.Y.; Zhou, J.; Jiao, B.N. A fluorescent aptasensor for ochratoxin A detection based on enzymatically generated copper nanoparticles with a polythymine scaffold. Microchim. Acta 2019, 186, 199. [Google Scholar] [CrossRef]
  47. Bi, X.Y.; Luo, L.J.; Li, L.B.; Liu, X.H.; Chen, B.N.; You, T.Y. A FRET-based aptasensor for ochratoxin A detection using graphitic carbon nitride quantum dots and CoOOH nanosheets as donor-acceptor pair. Talanta 2020, 218, 121159. [Google Scholar] [CrossRef] [PubMed]
  48. Pacheco, J.G.; Castro, M.; Machado, S.; Barroso, M.F.; Nouws, H.P.A.; Delerue-Matos, C. Molecularly imprinted electrochemical sensor for ochratoxin A detection in food samples. Sens. Actuators B Chem. 2015, 215, 107–112. [Google Scholar] [CrossRef]
  49. Wang, C.K.; Tan, R.; Li, J.Y.; Zhang, Z.X. Exonuclease I-assisted fluorescent method for ochratoxin A detection using iron-doped porous carbon, nitrogen-doped graphene quantum dots, and double magnetic separation. Anal. Bioanal. Chem. 2019, 411, 2405–2414. [Google Scholar] [CrossRef]
  50. Shao, X.L.; Zhu, L.J.; Feng, Y.X.; Zhang, Y.Z.; Luo, Y.B.; Huang, K.L.; Xu, W.T. Detachable nanoladders: A new method for signal identification and their application in the detection of ochratoxin A (OTA). Anal. Chim. Acta 2019, 1087, 113–120. [Google Scholar] [CrossRef]
  51. Wei, Y.; Zhang, J.; Wang, X.; Duan, Y.X. Amplified fluorescent aptasensor through catalytic recycling for highly sensitive detection of ochratoxin A. Biosens. Bioelectron. 2015, 65, 16–22. [Google Scholar] [CrossRef] [PubMed]
  52. Wang, C.K.; Dong, X.Y.; Liu, Q.; Wang, K. Label-free colorimetric aptasensor for sensitive detection of ochratoxin A utilizing hybridization chain reaction. Anal. Chim. Acta 2015, 860, 83–88. [Google Scholar] [CrossRef] [PubMed]
Scheme 1. Preparation of MnCO3NS/CF composite and OTA imprinted electrode.
Scheme 1. Preparation of MnCO3NS/CF composite and OTA imprinted electrode.
Biosensors 13 00760 sch001
Figure 1. (A,B) SEM images of MnCO3NS/CF composite at different magnifications.
Figure 1. (A,B) SEM images of MnCO3NS/CF composite at different magnifications.
Biosensors 13 00760 g001
Figure 2. (A) XRD patterns of MnCO3NS and MnCO3NS/CF composite (Six obvious XRD peaks at 24.08°, 31.79°, 37.79°, 41.93°, 45.07° and 51.36° corresponded to (012), (104), (110), (113), and (204) planes, respectively) and (B) Raman spectra of MnCO3NS and MnCO3NS/CF composite (G band is the in-plane vibrations of sp2 hybridization of carbon atoms and D band is known as the irregularity band or the defect band).
Figure 2. (A) XRD patterns of MnCO3NS and MnCO3NS/CF composite (Six obvious XRD peaks at 24.08°, 31.79°, 37.79°, 41.93°, 45.07° and 51.36° corresponded to (012), (104), (110), (113), and (204) planes, respectively) and (B) Raman spectra of MnCO3NS and MnCO3NS/CF composite (G band is the in-plane vibrations of sp2 hybridization of carbon atoms and D band is known as the irregularity band or the defect band).
Biosensors 13 00760 g002
Figure 3. (A) XPS survey spectrum of MnCO3NS/CF composite and high-resolution spectra of (B) Mn2p (red line: Mn2p1/2, yellow line: Mn2p3/2) (C) O1s (red line: O-Mn, yellow line: CO32−, blue line: C-O) and (D) C1s (red line: C-O, yellow line: C-C, green line: C-Mn).
Figure 3. (A) XPS survey spectrum of MnCO3NS/CF composite and high-resolution spectra of (B) Mn2p (red line: Mn2p1/2, yellow line: Mn2p3/2) (C) O1s (red line: O-Mn, yellow line: CO32−, blue line: C-O) and (D) C1s (red line: C-O, yellow line: C-C, green line: C-Mn).
Biosensors 13 00760 g003
Figure 4. (A) CV curves (arrow indicates potential scanning direction) and (B) EIS responses at (a) bare GCE, (b) MnCO3NS/GCE, (c) MnCO3NS/CF/GCE.
Figure 4. (A) CV curves (arrow indicates potential scanning direction) and (B) EIS responses at (a) bare GCE, (b) MnCO3NS/GCE, (c) MnCO3NS/CF/GCE.
Biosensors 13 00760 g004
Figure 5. (A) 100.0 mmol L−1 Py polymerization containing 25.0 mmol L−1 OTA on MnCO3NS/CF/GCE (Scan rate: 100 mV s−1) (arrow indicates potential scanning direction), (B) Differential pulse voltammograms (DPVs) of MIP and NIP electrodes: (a) in presence of PBS solution, (b) NIP/MnCO3NS/CF/GCE in presence of 0.5 nmol L−1 OTA and (c) MIP/MnCO3NS/CF/GCE in presence of 0.5 nmol L−1 OTA, (C) DPVs of different molecularly imprinting electrodes (a) MIP/bare GCE, (b) MIP/MnCO3NS/GCE and (c) MIP/MnCO3NS/CF/GCE.
Figure 5. (A) 100.0 mmol L−1 Py polymerization containing 25.0 mmol L−1 OTA on MnCO3NS/CF/GCE (Scan rate: 100 mV s−1) (arrow indicates potential scanning direction), (B) Differential pulse voltammograms (DPVs) of MIP and NIP electrodes: (a) in presence of PBS solution, (b) NIP/MnCO3NS/CF/GCE in presence of 0.5 nmol L−1 OTA and (c) MIP/MnCO3NS/CF/GCE in presence of 0.5 nmol L−1 OTA, (C) DPVs of different molecularly imprinting electrodes (a) MIP/bare GCE, (b) MIP/MnCO3NS/GCE and (c) MIP/MnCO3NS/CF/GCE.
Biosensors 13 00760 g005
Figure 6. Effect of (A) pH, (B) mole ratio, (C) desorption time, (D) scan cycle on signals of DPVs (in the presence of 0.5 nmol L−1 OTA) (n = 6).
Figure 6. Effect of (A) pH, (B) mole ratio, (C) desorption time, (D) scan cycle on signals of DPVs (in the presence of 0.5 nmol L−1 OTA) (n = 6).
Biosensors 13 00760 g006
Figure 7. DPVs with different OTA amount at MIP/MnCO3NS/CF/GCE in pH 7.0 of PBS. Inset: OTA’s calibration curve (from 0.01 nmol L−1 to 1.0 nmol L−1).
Figure 7. DPVs with different OTA amount at MIP/MnCO3NS/CF/GCE in pH 7.0 of PBS. Inset: OTA’s calibration curve (from 0.01 nmol L−1 to 1.0 nmol L−1).
Biosensors 13 00760 g007
Table 1. Comparison of MIP/MnCO3NS/CF/GCE with the reported methods for OTA detection.
Table 1. Comparison of MIP/MnCO3NS/CF/GCE with the reported methods for OTA detection.
MaterialLinear Range
(M, mol L−1)
LOD
(M, mol L−1)
Ref.
Aptasensor3.6 × 10−10–6.9 × 10−103.6 × 10−10[43]
SERS aptasensor1.0 × 10−10–4.0 × 10−83.0 × 10−11[44]
Au NPs/PIL-FMNS/CNT-MoS25.0 × 10−7–15.0 × 10−61.4 × 10−8[33]
Fluorescence quenching/AuNPs5.0 × 10−9–1.0 × 10−74.8 × 10−9[45]
CuNPs2.5 × 10−9–2.5 × 10−72.0 × 10−9[46]
g-CNQDs1.0 × 10−9–1.4 × 10−75.0 × 10−10[47]
MIP-MWCNTs5.0 × 10−8–1.0 × 10−64.1 × 10−9[48]
NGQDs-Apt1.0 × 10−8–5.0 × 10−62.3 × 10−9[49]
Graphene oxide0.0–2.0 × 10−71.0 × 10−10[50]
Fluorescent aptasensor0.0–1.0 × 10−62.0 × 10−8[51]
Colorimetric aptasensor1.0 × 10−11–3.2 × 10−81.0 × 10−11[52]
MIP/MnCO3NS/CF/GCE1.0 × 10−11–1.0 × 10−92.0 × 10−12This study
Table 2. Recovery results of OTA in apple juice (n = 6).
Table 2. Recovery results of OTA in apple juice (n = 6).
SampleAdded OTA
(nmol L−1)
Found OTA
(nmol L−1)
* Recovery
(%)
Apple Juice-0.307 ± 0.001-
0.1000.406 ± 0.00399.75 ± 0.06
0.3000.608 ± 0.004100.17 ± 0.08
0.5000.808 ± 0.002100.12 ± 0.05
* Recovery = Found OTA, nmol L−1/Real OTA, nmol L−1.
Table 3. k and k′ values of OTA imprinted electrodes (MIP/MnCO3NS/CF/GCE and NIP/MnCO3NS/CF/GCE).
Table 3. k and k′ values of OTA imprinted electrodes (MIP/MnCO3NS/CF/GCE and NIP/MnCO3NS/CF/GCE).
MIPNIP
I (µA)kI (µA)kk′
OTA9.50-1.75--
OTB1.207.920.503.502.26
AFB11.009.500.404.382.17
AFB20.7512.670.305.832.17
CIT0.5019.000.208.752.17
CAT0.3031.670.1511.672.71
RES0.2047.500.1017.502.71
k = ∆IOTA/∆I interfering chemical and k′ = kMIP/kNIP.
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Mavioğlu Kaya, M.; Deveci, H.A.; Kaya, İ.; Atar, N.; Yola, M.L. The Electrochemical Detection of Ochratoxin A in Apple Juice via MnCO3 Nanostructures Incorporated into Carbon Fibers Containing a Molecularly Imprinting Polymer. Biosensors 2023, 13, 760. https://doi.org/10.3390/bios13080760

AMA Style

Mavioğlu Kaya M, Deveci HA, Kaya İ, Atar N, Yola ML. The Electrochemical Detection of Ochratoxin A in Apple Juice via MnCO3 Nanostructures Incorporated into Carbon Fibers Containing a Molecularly Imprinting Polymer. Biosensors. 2023; 13(8):760. https://doi.org/10.3390/bios13080760

Chicago/Turabian Style

Mavioğlu Kaya, Müge, Haci Ahmet Deveci, İnan Kaya, Necip Atar, and Mehmet Lütfi Yola. 2023. "The Electrochemical Detection of Ochratoxin A in Apple Juice via MnCO3 Nanostructures Incorporated into Carbon Fibers Containing a Molecularly Imprinting Polymer" Biosensors 13, no. 8: 760. https://doi.org/10.3390/bios13080760

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop