Abstract
This work presents the development of disposable biosensors used in the determination of biogenic amines. The biosensors were fabricated using diamine oxidase (DAOx) or monoamine oxidase (MAOx) enzyme- and platinum nanoparticle (PtNP)-modified screen-printed carbon electrodes (SPCE). The morphological and electrochemical properties of the biosensors were examined by scanning electron microscopy, energy-dispersive X-ray spectroscopy, electrochemical impedance spectroscopy, and cyclic voltammetry measurements. Amperometric measurements indicated that the DAOx/PtNP/SPCE biosensor responded to histamine, putrescine, cadaverine, spermine, spermidine, β-phenylethylamine, tryptamine, and tyramine; however, its MAOx-based counterpart showed no response towards putrescine and cadaverine. A performance comparison of two biosensors indicated that the one based on DAOx had a linear concentration range from 5.3 × 10− 7 to 7.2 × 10− 5 M and the other based on MAOx from 3.9 × 10− 7 to 7.6 × 10− 5 M for tyramine. The sensitivities of the DAOx- and MAOx-based biosensors towards tyramine were 24.8 µA mM− 1 and 46.1 µA mM− 1, respectively. The proposed biosensors were tested for analysis of blue cheese sample spiked with known concentration of tyramine for the verification of biosensor applicability for real samples.
Graphic abstract
Similar content being viewed by others
Explore related subjects
Discover the latest articles, news and stories from top researchers in related subjects.Avoid common mistakes on your manuscript.
Introduction
Biogenic amines (BAs) are low molecular weight organic bases. These amines are mainly formed as a consequence of microbial decarboxylation of amino acids [1, 2]. The main BAs present in food products are histamine, putrescine, cadaverine, spermine, spermidine, β-phenylethylamine, tryptamine, and tyramine [3]. Biogenic amine formation in food products may occur due to inappropriate processing and storage conditions and subsequent microbial contamination. Therefore, the level of BAs in food can be used as a chemical indicator of spoilage [4]. Moreover, the ingestion of food containing high amounts of these amines can cause health problems [5]. The level of BAs in food products needs to be strictly controlled due to their toxicological risk and importance in food quality. For these reasons, the development of rapid, accurate, and practical methods for BA determination is becoming increasingly demanded.
Various analytical methods such as high-performance liquid chromatography [6], thin layer chromatography [7], gas chromatography [8], capillary zone electrophoresis [9] and electrochemical sensor and biosensors [10,11,12,13,14] have been reported to monitor the level of BAs. Amperometric biosensors offer several advantages over traditional chromatographic techniques for BA determination in terms of low cost, rapid response, high sensitivity and construction simplicity [15, 16]. Due to these reasons, nowadays, there is a great interest in the development of practical and reliable biosensors for the analysis of food products to guarantee their composition, safety, quality and traceability in accordance with regulatory legislation and consumer demands [17, 18].
The biosensors reported for the determination of BAs are generally based on the use of amine oxidase enzymes. These enzymes catalyze the conversion of the biogenic amines to the corresponding aldehyde, NH3, and H2O2 [19]. In these biosensors, the consumption of O2 [20] or the generation of H2O2 [21] can be monitored to quantify BAs.
Metal nanoparticles (MNP), especially gold and platinum nanoparticles (PtNP), have been widely used in the fabrication of electrochemical biosensors to improve their analytical performance characteristics [22, 23]. This is because MNP exhibit unique properties such as large effective surface area, strong catalytic properties that facilitate electron transfer between the electrode surface and biomolecule, good adsorption ability for biomolecule immobilization, and high surface activity [23]. Previous studies have indicated that PtNP possess excellent catalytic capabilities towards the oxidation and reduction of H2O2 [24]. Moreover, PtNP can provide biocompatible platforms for enzymes which is important for keeping their biologic activities [25].
Disposable screen-printed electrodes (SPEs) are planar sensor systems fabricated by the printing of conductive ink onto ceramic or plastic support [26]. They have important advantages such as mass production capabilities, low cost, portability, and practical use [27]. The modification of SPEs with MNP is a practical approach for the development of more sensitive amperometric biosensors [26].
Herein we report the construction and application two biogenic amine biosensors based on DAOx or MAOx enzyme- and PtNP-modified SPCEs for the rapid, practical, sensitive, and selective analysis of BAs. A comparison of the analytical performances of two biogenic amine biosensors is also presented and discussed. PtNP were grown on SPCEs using a one‐step electrodeposition process and these electrodes were then modified with DAOx or MAOx for the development of the biosensors. The experimental conditions which can effect the biosensors performance were optimized and the analytical characteristics of both biosensors were described. The practical use of both biosensors in real-sample analysis was also performed.
Results and discussion
Optimization of electrode surface composition
The electrodeposition of PtNP on SPCE was performed in an electroplating bath consisted of 2 mM H2PtCl6 and 0.1 M HCl [28], making a total volume of 5 cm3. The bare SPCE was immersed in the plating bath, and a constant potential was applied under stirring condition. To optimize the electrodeposition step, constant potentials of − 0.20 V, − 0.30 V, and − 0.40 V and time intervals of 450 and 300 s were investigated. DAOx was immobilized onto all electrodes fabricated with different platinum electrodeposition procedures and tyramine responses of these biosensors were investigated. The highest tyramine response was obtained with the biosensor fabricated with the modified electrode at which platinum was electrodeposited at a constant potential of − 0.40 V for 450 s. Therefore, these conditions were selected as the optimal for the PtNP electrodeposition.
Surface morphology
Scanning electron microscopy (SEM) was used to characterize the morphologies of (a) bare SPCE, (b) PtNP/SPCE, (c) DAOx/PtNP/SPCE, and (d) MAOx/PtNP/SPCE electrodes during stepwise modification. As shown in Fig. 1b, after the electrodeposition of PtNP, the nanoparticles covered the electrode surface and PtNP/SPCE had larger surface compared with the bare SPCE (Fig. 1a). Moreover, the spherical structure of the electrodeposited PtNP can be observed at electrode surface. The corresponding image slightly changed and a cloudy appearance was obtained when DAOx was immobilized on PtNP/SPCE (Fig. 1c). After the immobilization of MAOx onto PtNP/SPCE, the SEM image changed significantly (Fig. 1d). These changes observed in SEM images of enzyme modified electrodes can be attributed to the immobilization of the enzymes onto the electrode surface. Similar results were reported in the literature for DAOx- and MAOx-modified electrodes [14, 16].
Energy-dispersive X-ray spectroscopy (EDX) analysis was utilized to investigate the surface composition of PtNP/SPCE. Figure 1e depicts the EDX spectrum of PtNP/SPCE. The peak corresponding to the Pt element indicated that the PtNP were successfully electrodeposited on the surface of bare SPCE, which supports the SEM results.
Electrochemical characteristics of the modified electrodes
Cyclic voltammetry (CV) and electrochemical impedance spectroscopy (EIS) were used to characterize the modification of the electrode in 5 mM Fe(CN)63 −/4 − and 0.1 M KCl solution. Figure 2 compares the CV response at bare SPCE (a) and PtNP/SPCE (b) obtained at a scan rate of 50 mV s− 1 in the above solution, respectively. At the bare SPCE (curve a), oxidation and reduction peaks corresponding to the redox behaviour of ferricyanide–ferrocyanide couple was observed with a peak to peak separation (ΔEp) of 288 mV. After modified with PtNP, the anodic and cathodic peak currents were increased (curve b), indicating PtNP can improve the surface area of the electrode [29]. The electroactive surface area of the electrodes was estimated with CV according to the Randles–Sevcik equation [30]:
In this equation, n is the number of electrons transferred (n = 1), A refers to the electroactive surface area of the electrode (cm2). D is the diffusion coefficient of the molecule in solution (6.7 × 10− 6 cm2 s− 1), ν refers to the scan rate (0.05 V s− 1) and C is the concentration of the prob molecule in the bulk solution (5 mM). By applying the Randles–Sevcik equation, the calculated electroactive surface areas were 0.114 cm2 and 0.164 cm2 for SPCE and PtNP/SPCE, respectively. In comparison with the bare SPCE, the electroactive surface area of the PtNP/SPCE was increased by about 1.4 times. Furthermore, the peak to peak separation (ΔEp = 239 mV) decreased suggesting that the modification of the electrode surface with PtNP increased the electron transfer between the electrode surface and solution due to the increase in surface to volume ratio as a result of large surface area provided by the PtNP.
Figure 3 displays the EIS of the electrodes obtained in 5 mM Fe(CN)63 −/4 − and 0.1 M KCl solution. It can be seen from the figure that the electron transfer resistance (semicircle diameter, Rct) value of bare SPCE (1660 Ω) (curve a) remarkably decreased when the electrode was modified with PtNP (35.2 Ω) (curve b). This result indicates that the PtNP form high electron conduction pathways between the electrode and electrolyte and obviously improve the diffusion of ferricyanide toward the electrode surface [31].
Optimization of experimental parameters
Working potential
Amine oxidase enzymes catalyze the conversion of the biogenic amines to the corresponding aldehyde, NH3, and H2O2. H2O2 enzymatically generated from the BAs in the presence of DAOx or MAOx (Eq. (1)) is oxidized to O2 (Eq. (2)), and the current response obtained is directly proportional to the concentration of the corresponding biogenic amine [32]. The electrochemical reactions involved in response mechanism of the DAOx/PtNP/SPCE and MAOx/PtNP/SPCE biosensors are given below:
The working potential has a great effect on biosensor performance since it contributes to its sensitivity and selectivity. Figure 4 shows the cyclic voltammograms of (a) SPCE, (b) PtNP/SPCE, and (c) DAOx/PtNP/SPCE taken in 0.05 M BR buffer solution containing 0.1 M KCl (pH 7.0) and 0.1 mM H2O2 at a scan rate of 50 mV s− 1. As can be seen the peak currents recorded at PtNP/SPCE and DAOx/PtNP/SPCEs are higher than the currents recorded at SPCE and the oxidation process of H2O2 starts at about + 0.40 V.
Due to the CV results, the amperometric response of DAOx/PtNP/SPCE to tyramine was investigated at a constant tyramine concentration of 0.02 mM between + 0.20 and + 0.60 V to determine the optimum working potential (Fig. 5). The response current increased as the potential becomes more positive from + 0.20 to + 0.60 V, and the highest sensitivity was obtained at + 0.60 V. However, a working potential of + 0.50 V was selected as the working potential to decrease the effect of possible interferences.
pH
DAOx and MAOx enzymes catalyze the oxidative deamination of various BAs. Therefore, the influence of buffer pH on the amperometric responses of DAOx/PtNP/SPCE and MAOx/PtNP/SPCE biosensors was investigated in 0.05 M BR buffer solution at constant biogenic amine concentration for various BAs (histamine, cadaverine, putrescine, β-phenylethylamine, tryptamine, tyramine, spermine, and spermidine) widely present in food products. For the DAOx/PtNP/SPCE biosensor, optimum pH was found to be 8.0 for histamine and putrescine; 7.5 for cadaverine; 8.5 for tryptamine; 8.0 for tyramine; 8.5 for spermine, and β-phenylethylamine and 10.5 for spermidine (Fig. 6).
In case of MAOx/PtNP/SPCE biosensor, pH 7.5 for tryptamine, 9.5 for tyramine, spermine, and β-phenylethylamine, and 10.0 for histamine and spermidine were obtained as the optimum values for the buffer pH. These optimum pH values were used in the determination of analytical characteristics of both biosensors and chronoamperometric responses were measured at optimum pH of each amine.
Performance parameters and substrate specificity
Chronoamperometry was used to determine the responses of DAOx/PtNP/SPCE and MAOx/PtNP/SPCE biosensors to histamine, cadaverine, putrescine, β-phenylethylamine, tryptamine, tyramine, spermine, and spermidine and i–t graphs were recorded for each biogenic amine at its optimum pH. Figure 7 depicts the amperometric responses of DAOx/PtNP/SPCE and MAOx/PtNP/SPCE biosensors to consecutive additions of tyramine at + 0.50 V and the corresponding calibration curves of the calculated current differences (ΔI) vs. the concentration of tyramine determined by both biosensors. DAOx/PtNP/SPCE biosensor displayed a linear relationship between the current and tyramine concentration in the range of 5.3 × 10− 7–7.2 × 10− 5 M with a sensitivity of 24.8 µA mM− 1. The limit of detection (LOD) was calculated according to the 3sb/m criteria, where m represents the slope of the calibration graph and sb represents the standard deviation of the amperometric responses from different solutions of tyramine at the concentration level corresponding to the lowest concentration of the calibration curve [33, 34]. The LOD of the DAOx-based biosensor was found to be 2.5 × 10− 7 M for tyramine. For the MAOx/PtNP/SPCE biosensor, the linear dynamic range of the tyramine determination was from 3.9 × 10− 7–7.6 × 10− 5 M. The detection limit and sensitivity of this biosensor were found to be 2.1 × 10− 7 M and 46.1 µA mM− 1, respectively. Both biosensors exhibited a rapid electrochemical response, reaching 95% of the steady-state current within 5 s after each tyramine addition.
Table 1 presents the linear dynamic ranges and sensitivities obtained from corresponding calibration graphs for all BAs investigated. As can be seen from the table, both biosensors exhibited a wide linear working range and good sensitivity for tyramine determination. DAOx/PtNP/SPCE biosensor showed the highest sensitivity to spermine (39.8 μA mM− 1) with a linear dynamic range of 3.8 × 10− 7–9.9 × 10− 6 M and LOD of 1.1 × 10− 7 M. This biosensor also exhibited high sensitivity to spermidine (37.7 μA mM− 1) with a wider linear dynamic range of 2.9 × 10− 7–4.6 × 10− 5 M. Although a very narrow linear dynamic range (2.7 × 10− 6–9.8 × 10− 5 M) was obtained for tryptamine, the sensitivity of 24.2 µA mM− 1 was quite satisfactory. This biosensor responded to histamine (5.2 μA mM− 1), putrescine (4.5 μA mM− 1), and cadaverine (5.4 μA mM− 1) with a lower sensitivity. However, wide linear dynamic ranges were obtained for histamine (3.8 × 10− 7–1.1 × 10− 5 M), putrescine (4.9 × 10− 7–2.3 × 10− 5 M), and cadaverine (9.0 × 10− 7–1.1 × 10− 5). DAOx/PtNP/SPCE biosensor showed the lowest sensitivity to β-phenylethylamine (0.9 μA mM−1) with a linear dynamic range of 9.5 × 10− 6–1.8 × 10− 4 M. It can be concluded that DAOx/PtNP/SPCE biosensor can be used in the determination of all BAs investigated.
In case of MAOx/PtNP/SPCE biosensor, no response was obtained for putrescine and cadaverine. Contrary to DAOx/PtNP/SPCE biosensor, a very wide linear dynamic range of 7.9 × 10− 8–8.0 × 10− 3 M was obtained with MAOx-based biosensor for tryptamine with a high sensitivity of 38.6 µA mM− 1. On the other hand, this biosensor responded to spermine (18.1 μA mM− 1; 4.9 × 10− 7–1.6 × 10− 4 M) and spermidine (32.3 µA mM− 1; 7.9 × 10− 7–1.0 × 10− 4 M) with good sensitivity and wide linear dynamic range. However, the lower sensitivities and narrow linear ranges were obtained for histamine (1.9 μA mM− 1; 3.3 × 10− 6–4.9 × 10− 5 M) and β-phenylethylamine (0.6 µA mM− 1; 2.4 × 10− 5–5.9 × 10− 4 M). These results indicated that MAOx based can be used in the determination of histamine, β-phenylethylamine, tryptamine, tyramine, spermine, and spermidine.
The repeatability and reproducibility of the DAOx/PtNP/SPCE and MAOx/PtNP/SPCE biosensors were explored using tyramine as a substrate. Five successive calibration curves were plotted under the optimum experimental conditions using the same biosensor to evaluate the repeatability. The change observed in sensitivities between the 1st and the 5th calibration in terms of relative standard deviation (RSD) was 8% and 6% for with DAOx/PtNP/SPCE and MAOx/PtNP/SPCE biosensors, respectively. This result indicated the satisfactory repeatability of the biosensors. In case of reproducibility, calibration curves were obtained, using five different similarly fabricated electrodes. The RSD values obtained with DAOx/PtNP/SPCE and MAOx/PtNP/SPCE biosensors were 6.5% and 4.9%, respectively. It can be concluded that the biosensors exhibited good reproducibility. The operational stability of the presented biosensors was also investigated by the measurements of the biosensor response to 0.02 mM tyramine. The presented DAOx/PtNP/SPCE (RSD < 10%) and MAOx/PtNP/SPCE (RSD < 7%) biosensors showed good operational stability after 30 successive measurements.
Table 2 shows the analytical characteristics of various previously reported biogenic amine biosensors. A comparison of the data presented in Tables 1 and 2 indicates that DAOx/PtNP/SPCE and MAOx/PtNP/SPCE biosensors offered a higher sensitivity and lower detection limit for the BAs investigated than most of the previous biogenic amine biosensors.
Interference effect
The interference effect of various amino acids on the tyramine response of the biosensors (histidine, ornithine, tyrosine, lysine, tryptophan, arginine, and β-phenylethylamine) was investigated. The amino acids studied were those involved in the biosynthesis of BAs [19]. The interference effect was determined by comparison of the response obtained for 0.1 mM standard tyramine solution vs. the response obtained for the same concentration of standard amino acid solutions and presented in Table 3 in terms of interference percentage.
As seen from the Table, β-phenylethylamine showed a slight effect (< 3%) on the response of DAOx/PtNP/SPCE and MAOx/PtNP/SPCE biosensors. The interference effect of tyrosine, arginine, histidine, and ornithine was < 10% at both biosensors. In case of lysine 12.0% interference was observed for DAOx/PtNP/SPCE. However, the effect of lysine was smaller at MAOx/PtNP/SPCE (11.3%). On the other hand, tryptophan caused 23.4% and 28.3% interference on the tyramine response currents of DAOx/PtNP/SPCE and MAOx/PtNP/SPCE biosensors, respectively. This high interference effect of tryptophan can be attributed to its electrochemical oxidation at the operating potential [38]. It can be concluded that the presence of tryptophan in real samples can affect the tyramine response of the biosensor.
Real-sample analysis
The performance of the DAOx/PtNP/SPCE vs. MAOx/PtNP/SPCE biosensors was evaluated using cheese sample that spiked with known concentrations of tyramine. Tyramine was selected as the reference amine for the recovery tests due to the high sensitivities and wide linear dynamic ranges obtained with both biosensors for tyramine. Moreover, tyramine is one of the most common BAs present in cheese. For this purpose, 50 mm3 of the cheese extract was added to the electrochemical cell containing 5 cm3 of BR buffer solution and standard addition was performed to determine the tyramine level in cheese sample. However, both biosensors detected no tyramine in cheese sample. Therefore, the recovery tests were performed by spiking certain amounts of standard tyramine solution to the cheese extract to investigate the applicability of the presented biosensors. The tyramine levels in spiked sample were determined by standard addition method in triplicate. The recoveries of tyramine from spiked cheese sample determined by both biosensors are presented in Table 4. The recoveries obtained for tyramine were about 100%, indicating that the reliability of the biosensor method is good, and the developed biosensors can be used for tyramine determination in cheese samples.
Conclusion
Two amperometric biosensors based on DAOx- or MAOx-immobilized PtNP-modified SPCEs were developed for the determination of BAs and their analytical performance characteristics were compared. DAOx/PtNP/SPCE biosensor responded to all BAs investigated; however, its MAOx-based counterpart did not respond to putrescine and cadaverine. MAOx/PtNP/SPCE biosensor showed the highest sensitivity to tyramine which was 1.9 times higher than the sensitivity obtained with DAOx-based biosensor. Both biosensors showed low sensitivity to β-phenylethylamine and the linear dynamic range obtained with DAOx/PtNP/SPCE for tryptamine was narrow. DAOx/PtNP/SPCE and MAOx/PtNP/SPCE biosensors exhibited higher sensitivity and lower detection limit for the BAs than most of the earlier biogenic amine biosensors. Moreover, these biosensors possess the advantage of easy and rapid construction and which is critical in routine analysis. The presented biosensors successfully applied for tyramine determination in spiked cheese sample and good recoveries were obtained.
Experimental
Human recombinant MAOx A (≥ 10 unit/mg protein, ≥ 3 mg protein/cm3, EC 1.4.3.4.), DAOx from porcine kidney (≥ 0.05 unit/mg solid, EC 1.4.3.22), histamine dihydrochloride, potassium chloride, chloroplatinic acid (H2PtCl6·6H2O), cadaverine dihydrochloride, β‐phenylethylamine hydrochloride, spermine, spermidine, tryptamine, putrescine dihydrochloride, tyramine, boric acid, acetic acid, phosphoric acid, potassium hexacyanoferrate(III), potassium hexacyanoferrate(II) trihydrate, Nafion® perfluorinated resin solution, l‐histidine, l‐tyrosine, l‐tryptophan, l‐arginine, l‐lysine, and l-phenylalanine were supplied from Sigma-Aldrich (Sigma-Aldrich, USA). l-Ornithine hydrochloride was purchased Acros Organics. Deionized water obtained from ELGA Purelab Option-S System was used throughout the experiments. SPCEs with working electrodes of 4 mm in diameter (model C110) were bought from Dropsens (Llanera, Spain).
The electrodeposition of PtNP and electrochemical measurements were performed using an Ivium CompactStat electrochemical analyzer (Ivium Technologies, Netherlands) at room temperature. The amperometric measurements were carried out at + 0.50 V in 0.05 M Britton–Robinson (BR) buffer solution. After the working electrode reached the steady state (background current), aliquots of tyramine stock solution were successively added to the stirred BR buffer and the steady-state current values recorded. In amperometric measurements, the variation (Δi) between the steady-state current and background current was marked as the response current. Cyclic voltammetry and electrochemical impedance spectroscopy measurements were obtained in the presence of 5.0 mM K3[Fe(CN)6]/K4[Fe(CN)6] (1:1) and 0.1 M KCl solution. A frequency range of 100 kHz−0.1 Hz was utilized with a potential amplitude of 5 mV for the EIS measurements. Scanning electron microscopy images and energy-dispersive X-ray spectroscopy spectra were obtained by using FEI, Quanta 450 FEG model scanning electron microscope, and Bruker detector, respectively.
Fabrication of the biosensors
The SPCE was immersed in 1.0 M H2SO4 solution and activated by electrochemical cyclic scanning method with 5 scans at a scanning speed of 100 mV s− 1 and potential range from − 0.40 to + 0.60 V. Electrodeposition of PtNP on SPCE was carried out in an electroplating bath containing 2 mM H2PtCl6 and 0.1 M HCl. The activated SPCE was immersed in the plating bath, and a constant potential of − 0.40 V was applied for 450 s. For the fabrication of the biogenic amine biosensors, 5 mg of DAOx was dissolved in 1 cm3 of 0.05 M BR buffer solution (pH 7.2) (1.0 U cm− 3) and 5 mm3 of the enzyme solution was pipetted on the surface of the PtNP/SPCE. After drying for 2 h at 4 ℃ in refrigerator, a 0.25% Nafion solution was dropped on the electrode surface as a protective membrane. In case of MAOx-based biosensor, 5 mm3 enzyme (30 U cm− 3) was immobilized onto the PtNP/SPCE surface and the electrode surface was further modified with Nafion solution for the fabrication of the biosensor.
Sample preparation
2 g of blue cheese sample obtained from a local market was weighed and homogenized. 10 cm3 of 0.40 M HClO4 was added to the homogenate and blended for 10 min. The blend was centrifuged for 10 min at 4100 rpm. The supernatant was diluted to 1:25 with BR buffer solution and the cheese was stored at − 18 ℃ in refrigerator.
References
Önal A (2007) Food Chem 103:1475
Nalazek-Rudnicka K, Wasik A (2017) Monatsh Chem 148:1685
Erim FB (2013) TrAC Trends Anal Chem 52:239
Jairath G, Singh PK, Dabur RS, Rani M, Chaudhari M (2015) J Food Sci Technol 52:6835
Alvarez MA, Moreno-Arribas MV (2014) Trends Food Scı Tech 39:146
Peng JF, Fang KT, Xie DH, Ding B, Yin JY, Cui XM, Zhang Y, Liu JF (2008) J Chromatogr A 1209:70
Tao Z, Sato M, Han Y, Tan Z, Yamaguchi T, Nakano T (2011) Food Control 22:1154
Önal A, Tekkeli SEK, Önal C (2013) Food Chem 138:509
Kvasnička F, Voldřich M (2006) J Chromatogr A 1103:145
Henao-Escobar W, Del Torno-de RL, Domínguez-Renedo O, Alonso-Lomillo MA, Arcos-Martínez MJ (2016) Food Chem 190:818
Gumpu MB, Nesakumar N, Sethuraman S, Krishnan UM, Rayappan JBB (2014) Sens Actuators B Chem 199:330
Küçük A, Torul O (2018) Synth Met 237:23
Lee MY, Wu CC, Sari MI, Hsieh YH (2018) Electrochim Acta 283:772
Kaçar C, Erden PE, Dalkıran B, İnal EK, Kılıç E (2020) Anal Bioanal Chem 412:1933
Dalkıran B, Erden PE, Kaçar C, Kılıç E (2019) Electroanal 31:1324
Erden PE, Erdoğan ZÖ, Öztürk F, Koçoğlu İO, Kılıç E (2019) Electroanal 31:2368
Pérez-López B, Merkoçi A (2011) Trends Food Sci Tech 22:625
Zeng Y, Zhu Z, Du D, Lin Y (2016) J Electroanal Chem 781:147
Pérez S, Bartrolí J, Fàbregas E (2013) Food Chem 141:4066
Hernández-Cázares AS, Aristoy MC, Toldrá F (2011) J Food Eng 106:166
Apetrei I, Apetrei C (2016) Sensors 16:422
Mehmeti E, Stanković DM, Chaiyo S, Švorc Ľ, Ortner A, Kalcher K (2016) Monatsh Chem 147:1161
Turkmen E, Bas SZ, Gulce H, Yildiz S (2014) Electrochim Acta 123:93
Jiang X, Wu Y, Mao X, Cui X, Zhu L (2011) Sens Actuators B Chem 153:158
Li J, Yu J, Wei X, Liu R (2011) J Solid State Electr 15:1129
Barquero-Quirós M, Domínguez-Renedo O, Alonso-Lomillo MA, Arcos-Martínez MJ (2012) Microchim Acta 179:65
Xu S, Qin X, Zhang X, Zhang C (2015) Microchim Acta 182:1241
Zou Y, Xiang C, Sun LX, Xu F (2008) Biosens Bioelectron 23:1010
Eremia SA, Vasilescu I, Radoi A, Litescu SC, Radu GL (2013) Talanta 110:164
Wang J (2006) Analytical electrochemistry, 3rd edn. John Wiley & Sons Inc, Hoboken
Agrisuelas J, González-Sánchez MI, Valero E (2017) Sens Actuators B Chem 249:499
Lange J, Wittmann C (2002) Anal Bioanal Chem 372:276
Eguilaz M, Agüí L, Yanez-Sedeno P, Pingarron JM (2010) J Electroanal Chem 644:30
Serra B, Morales MD, Reviejo AJ, Hall EH, Pingarron JM (2005) Anal Biochem 336:289
Compagnone D, Isoldi G, Moscone D, Palleschi G (2001) Anal Lett 34:841
Telsnig D, Kalcher K, Leitner A, Ortner A (2013) Electroanal 25:47
Leonardo S, Campàs M (2016) Microchim Acta 183:1881
Fang B, Wei Y, Li M, Wang G, Zhang W (2007) Talanta 72:1302
Acknowledgements
We gratefully acknowledge the financial support (TUBITAK Project no.: 116Z159) of The Scientific and Technological Research Council of Turkey.
Author information
Authors and Affiliations
Corresponding author
Additional information
Publisher's Note
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Rights and permissions
About this article
Cite this article
Dalkıran, B., Kaçar, C., Can, E. et al. Disposable biosensors based on platinum nanoparticle-modified screen-printed carbon electrodes for the determination of biogenic amines. Monatsh Chem 151, 1773–1783 (2020). https://doi.org/10.1007/s00706-020-02707-1
Received:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s00706-020-02707-1