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. 2022 Feb 10;7(7):5982–5991. doi: 10.1021/acsomega.1c06295

The Application of Polyurethane-LiClO4 to Modify Screen-Printed Electrodes Analyzing Histamine in Mackerel Using a Voltammetric Approach

Muhammad Abdurrahman Munir †,*, Khairiah Haji Badri ‡,§, Lee Yook Heng , Ahlam Inayatullah , Eva Nurinda , Daru Estiningsih , Annisa Fatmawati , Veriani Aprilia , Nur Syafitri
PMCID: PMC8867486  PMID: 35224359

Abstract

graphic file with name ao1c06295_0013.jpg

Histamine is an important substance that can be applied as a parameter for allergic reactions and food freshness. This study develops a method to produce a histamine sensor based on electrodes modified using polyurethane-LiClO4. A sensor method was developed where this sensor was produced from polyurethane. The application of 4,4′-diphenylmethane diisocyanate (hard compound) and palm kernel oil-based monoester polyol (soft compound) to produce polyurethane (PU) based on bio-polyol. The addition of lithium perchlorate (LiClO4) was done in order to increase the conductivity of PU. The oxidation process was detected using cyclic voltammetry, whereas the electrochemical impedance spectroscopy was used to analyze the conductivity of the polymer. The polyurethane-LiClO4 was attached on a screen-printed electrode (SPE) within 45 min. Moreover, the 1% LiClO4-PU-SPE presented satisfactory selectivity for the detection of histamine in the pH 7.5 solution. The LiClO4-PU-SPE presented a good correlation coefficient (R = 0.9991) in the range 0.015–1 mmol·L–1. The detection limit was 0.17 mmol·L–1. Moreover, the histamine concentration of mackerel samples was detected by the PU-SEP-LiClO4. Several amine compounds were chosen to study the selectivity of histamine detection using SPE-PU-LiClO4. The interference was from several major interfering compounds such as aniline, cadaverine, hexamine, putrescine, and xanthine. The technique showed a satisfactory selective analysis compared to the other amines. A satisfactory recovery performance toward varying concentrations of histamine was obtained at 94 and 103% for histamine at 0.01 and 0.1 mmol·L–1, respectively. The application of PU-SEP-LiClO4 as an electrochemical sensor has a great prospect to analyze histamine content in fish mackerel as a consequence of PU-SEP-LiClO4 having good selectivity and simplicity.

1. Introduction

Nowadays, food security becomes the main attention of the food industry due to various foods that have been produced caused by the high demand. Several factors influence the stability of food content such as the presence of bacteria, the storage and packaging methods, and the production of chemical compounds such as biogenic amines, particularly histamine.1,2 Histamine analysis in foods draws huge attention from several researchers because of not only the capability to poison the consumers but also the stability of histamine to withstand inside foods during the cooking or heating process.3,4

Various methods have been developed by researchers in order to analyze histamine in various samples such as fish, meat, cheese, fruits, milk, etc. Liquid chromatography and gas chromatography are the popular techniques chosen by researchers based on their ability to determine histamine concentration. Furthermore, the ability of these techniques is unquestionable such as being very selective, sensitive, robust, and well established.59 However, these methods have several disadvantages such as being time-consuming, requiring various chemical reagents, high price, and the fact that merely people who study analytical chemistry can comprehend these machines. Furthermore, histamine is a less chromophore and unvaporized compound, thus the modification of histamine structure can be done by a derivatization process only.10,11

These issues can be solved by electrochemical sensor application. They are very fast, inexpensive, have fewer chemical materials, and are easily used. The approaches of these techniques are different compared to chromatography techniques. In order to detect histamine, the sensors require a specific receptor, biological (enzymes) receptors, or chemical receptors.12,13 Nevertheless, the biological receptor of the sensor known as biosensor offers instability and expensive test kits. Several studies reported the application of enzymes is unstable owing to many factors that can affect it such as temperature and pH. Several foods also contain metals that can work as an inhibitor to inhibit enzyme activity.1416 A chemical sensor is a better choice in order to avoid the use of biological receptors. Nowadays, screen-printed electrodes (SPEs) modified with conducting polymer have been developed for various electrochemical sensing. The SPE becomes the best solution owing to its frugal manufacture, tiny size, ability to be produced on a large scale, and can be applied for on-site detection.17,18 Polymers become an alternative to modify the screen-printed electrodes due to their electrical conductivity, ability to capture analyte by chemical/physical adsorption, large surface area, and making polymers that are very appealing materials from electrochemical perspectives.19 A natural polymer such as polyurethane has recently attracted analytical chemistry researchers owing to the fact that they have a prospect to be employed in electrochemical devices. Natural polymers have several properties that can be considered for electrochemical application such as easy handling during production, having no harm to the environment, low toxicity, cost effectiveness, and biodegradability.2022

Platinum, gold, and carbon are common materials used by researchers in order to modify electrodes.23,24 Furthermore, carbon, gold, and platinum are expensive and should be modified before being applied as electrochemical sensors. Lithium perchlorate (LiClO4) is an alternative in order to modify the conductivity of the polymer. Not only the price is cheaper but also the production of PU-LiClO4 is easy. In this study, LiClO4 was employed owing to having lattice energy. It contains cations and anions. Furthermore, the ionic conductivity is affected by the size where the current is produced by the diffusion rate of anions and cations. Thus, it can be concluded that not only LiClO4 is a good conductivity but also the production is easy. Furthermore, this material is a better solution compared to other materials (gold, carbon, platinum, and graphene) due to the interfacial resistance being low. Thus, LiClO4 can be diluted in most solvents due to possession of dissociation energy.25,26

Such advantages of SPE-PU-LiClO4 encourage us to construct a new electrode for electrochemical sensing, and no study was published on histamine detection using SPE-PU-LiClO4 by an electrochemical approach. Thus, this study can be considered as a new approach to electro-analysis of histamine. Histamine was then determined using a voltammetric approach. The sensor was applied to monitor the histamine concentration in fish mackerel.

2. Experimental Section

2.1. Materials and Preparation of SPE-PU-LiClO4

Palm kernel oil (PKO)p was supplied by UKM Technology Sdn. Bhd. through MPOB/UKM Station Plant, Pekan Bangi Lama, Selangor and prepared using Badri et al.’s method. 4,4-Diphenylmethane diisocyanate (MDI) was acquired from Cosmopolyurethane (M) Sdn. Bhd., Klang, Malaysia.27 Lithium perchlorate (LiClO4), polyethylene glycol (PEG) 400, and acetone solution were obtained from Sigma Aldrich Sdn. Bhd, Shah Alam and have been employed to produce SPE-PU-LiClO4. Film production was produced using a casting method.

In this work, 10.0 g of palm kernel oil (PKO) and 2.0 g of PEG 400 were dissolved in 10 mL of the solution of 30% acetone and then stirred at ambient temperature for 5 min to acquire a homogenized solution. Afterward, 10.0 g of MDI was dissolved in 10 mL of 30% acetone and stirred. The MDI solution was poured slowly into PKO and PEG 400 solution in order to control the exothermic reaction, and stirred until the homogenized solution was obtained. Various amounts of 1, 3, and 5% of lithium perchlorate (LiClO4) were employed and put into the mixture until a homogenized solution was acquired. The solution was poured onto the screen-printed electrode using the casting method and left at room temperature to dry the film. Thereby, SPE-PU-LiClO4 was obtained.

2.2. Instruments and Chemicals

Metrohm Autolab Electrochemical Workstation (UKM, Bangi, Malaysia) (Figure 1) was used to conduct cyclic voltammetry (CV), differential pulse voltammetry (DPV), and electrochemical impedance spectroscopy (EIS) analysis. All electrochemical experiments were performed using three electrodes as SPE-PU-LiClO4 as a working electrode, Ag/AgCl applied as a reference electrode, and platinum wire was employed as an auxiliary electrode. All experiments were conducted at ambient temperature. Histamine (HIS), cadaverine (CAD), and putrescine (PUT) were obtained (≥99% purity) from Sigma Aldrich Sdn. Bhd. The supporting electrolyte was potassium chloride (KCl 0.1 M) (Sigma Aldrich Sdn. Bhd). Sodium hydroxide (NaOH) (0.1 N) and hydrochloric acid (HCl) (0.1 N) were used to control the pH solution and obtained from Sigma Aldrich Sdn. Bhd. The application of 0.1 M disodium hydrogen phosphate (Na2HPO4) and 0.1 M sodium dihydrogen phosphate (NaH2PO4) was used to produce the phosphate buffer solution (PBS) (0.1 mol·L–1), and both materials were purchased from Sigma Aldrich Sdn. Bhd. All chemicals with analytical grade were employed during experiments. Solutions were produced using deionized water cleansed with a Milli-Q system and stored at 4 °C.

Figure 1.

Figure 1

(a) SPE-PU-LiClO4 and (b) instrument employed to analyze several techniques such as the CV, DPV, and EIS techniques. (Photograph courtesy of Muhammad Abdurrahman Munir. Copyright 2021).

2.3. Analytical Procedure and Real Sample Preparation

Histamine stock solution (10 mmol·L–1) was established by weighing histamine (111 mg) and dissolving in 100 mL of PBS (0.1 mol·L–1) at pH 7.5. A serial dilution was obtained from histamine stock solution ranging from 0.015 to 1 mmol·L–1. Each concentration of histamine standard was analyzed using the CV method in potential ranging from 0 to +1.0 V.

Fish mackerel samples were bought from a fish store in Dengkil, Malaysia, and stored in a fridge. Briefly, 5 g of fish sample was scaled and homogenized using PBS (0.1 mol·L–1) at pH 7.5 with 20 mL. The mixture was stirred for 5 min at 100 rpm and filtered using filter paper. Approximately 100 μL was transferred to a 10 mL volumetric flask and diluted to the tag with PBS (0.1 mol·L–1) to produce the specific volume. Afterward, two histamine levels of standard solutions were chosen (0.13 and 0.015 mmol·L–1) in order to study the proposed technique for histamine determination in fish samples.

3. Results and Discussion

3.1. Deposition of PU-LiClO4 at the SPE Surface

The CV and EIS techniques were applied to the electrochemical behavior of histamine. It was studied at unmodified and modified electrodes with various amounts of LiClO4. The purpose of LiClO4 addition is to increase the conductivity of PU. Thus, due to the PU porosity, the lithium was entrapped inside the PU pores. The examination applied several pH values ranging from 6 to 8 in PBS (0.1 mol·L–1). The investigations presented that the phosphate buffer was a satisfactory solution owing to the histamine appearance. Some studies mentioned that the application of PBS (0.1 mol·L–1) as a supporting electrolyte to detect histamine in samples is the best solution due to the fact that it offers a better analytical response, whereas the application of sodium hydroxide (NaOH) and hydrochloric acid (HCl) was not suggested by several studies due to the fact that it can reduce the selectivity of histamine detection.28,29 The various concentrations of PBS (pH 7.5) as the supporting electrolyte at 0.01, 0.05, 0.10, and 0.50 mol·L–1 were investigated. Nevertheless, the PBS levels did not disturb the histamine signal when detected using the CV method. Furthermore, the PBS (0.1 mol·L–1) at pH 7.5 was chosen in several studies and discovered to be suitable due to a good signal during histamine analysis providing better sensitivity,29 thus it was chosen for further electro-analysis.

The conductivity of PU-LiClO4 was measured by the alternating current (ac) EIS method as shown in Figure 2 using a Metrohm Autolab Electrochemical Workstation (UKM, Bangi, Malaysia) with a frequency ranging from 1 Hz to 10 MHz at 100 mV amplitude under room conditions (25 °C, 1 atm). The unmodified electrodes such as SPE and SPE-PU and modified SPE such as SPE-PU-LiClO4 with various concentrations of lithium perchlorate were analyzed using impedance spectroscopy in PBS (0.1 mol·L–1) at pH 7.5. The circuit model was fitted using Zviewer Analyzer Software.

Figure 2.

Figure 2

Spectra of the impedance of unmodified and modified electrodes in PBS (0.1 mol·L–1) at pH 7.5 after being analyzed using Zview Analyzer Software.

The electrical conductivity (σ) was calculated from the bulk resistance (Rb), determined from the equivalent circuit analysis by using the Zview analyzer software, and the polymer film thickness (l) was measured using thickness gauge calipers and contact area of the thin film (0.25 cm2), in accordance with the equation shown below.30 By using eq 1, the conductivity of PU and SPE were 5.8 × 10–5 S·cm–1 and 1.2 × 10–4 S·cm–1, respectively. Meanwhile, the conductivity of SPE-PU-LiClO4 was 1.6 × 10–4 S·cm–1 due to the incorporation of lithium perchlorate.

3.1. 1

Figure 3 presents the cyclic voltammograms of the unmodified electrodes such as SPE and SPE-PU and modified SPE such as SPE-PU-LiClO4 with various concentrations of lithium in KCl (0.1 mmol·L–1). The voltammogram of unmodified SPE and modified SPE was compared using a potential ranged at 0.0 to +1.0 V and a 0.05 V·s–1 scan rate. The voltammogram of the unmodified SPE and SPE-PU-LiClO4 exhibit identical redox couples. Furthermore, the current of SPE-PU-LiClO4 was smaller owing to the PU applied in this research being a natural polymer produced from palm kernel oil and exhibiting a weak electrochemical response owing to the conductivity being low.31 Furthermore, the addition of LiClO4 in this study was imperative in order to modify the conductivity of PU.

Figure 3.

Figure 3

Cyclic voltammograms of an unmodified electrode and modified electrode with various lithium perchlorates amount in 0.1 mmol·L–1 KCl.

Figure 3 reveals an oxidation reaction of bare SPE and SPE-PU-LiClO4 in KCl (0.1 mmol·L–1) with various concentrations of LiClO4 (1, 3, and 5%) that can be indicated as an anodic peak and appeared at +0.5 V. The analytical response of bare SPE and SPE-PU-LiClO4 ranged at −0.2 to +1.0 V, showing a specific potential at +0.5 V of both, whether the SPE and SPE-PU-LiClO4. The unmodified SPE gave a larger current due to the SPE surface produced from the material that can release a high electrical current.31 Furthermore, compared to the modified SPE, the signal gave a higher current owing to the addition of LiClO4. However, the application of LiClO4 in this study did not release an oxidation process owing to the material not dissolving in polyurethane but being entrapped inside the PU pores.

The cyclic voltammograms obtained can be used to evaluate the electron transfer during analysis using the Randles–Sevcik formula29

3.1. 2

where C is the histamine level applied, n is the electrons transferred, and D is the diffusivity of 0.1 mmol·L–1 KCl. Furthermore, the SPE has a surface area of 0.2 cm2 with 0.25 cm2 for PU-SPE-LiClO4 (0.5 × 0.5 cm). This area is called the geometric area of the working electrode. Thus, it can be seen that PU-SPE-LiClO4 has more surface area than the SPE. Furthermore, the concentration of surface area or symbolized as (τ) can be estimated using the equation below:

3.1. 3

where Ip is for the peak current, while A is for the region of the electrode, v is the scan rate, F is Faraday’s constant, R is the ideal gas constant, and T is the experimental absolute temperature.32 Thus, according to the obtained results, polyurethane was combined with 1% of LiClO4 in order to modify the screen-printed electrode. This modification was used for further studies such as a scan rate study, pH study, and analytical performance of the modified electrode.

3.2. Effect of Scan Rate

The scan rate was also studied using the cyclic voltammetry technique. This study wanted to investigate the anodic signal and potential of histamine at PU-SPE-LiClO4 if various scan rates were applied. Figure 4 presents the cyclic voltammograms of histamines (0.063 mmol·L–1) in PBS (0.1 mol·L–1) at pH 7.5 on PU-SPE-LiClO4, employing several scan rates (0.01–0.10 V·s–1). The peak current obtained shows a direct proportionality on the scan rate and potential applied, obtaining the equation ipa (μA) = 0.0551 + 214.58v (v in mV·s–1) and R2 = 0.9977, respectively. Thus, Figure 5a reveals that the histamine can be oxidized on the surface of the modified electrode.

Figure 4.

Figure 4

Cyclic voltammograms of histamine (0.063 mmol·L–1) in PBS (0.1 mol·L–1) at pH 7.5 on SPE-PU-LiClO4 for various scan rates ranging from 0.01 to 0.10 V·s–1.

Figure 5.

Figure 5

(a) Calibration curve of the histamine oxidative peak vs the scan rate (0.01–0.10 V·s–1) and (b) calibration curve between the current (μA) and potential applied (V).

The electrode involved in the process can be studied using the relationship between the scan rate, potential response, and anodic peak.33 Thus, the scan rate effects were studied in order to observe the histamine response during electrochemical analysis. The scan rates ranged from 0.01 to 0.10 V·s–1 using the CV technique. The obtained results show that the anodic peak of histamine increases when the scan rate (v) increases. The correlation can be described by the formula below:

3.2. 4

Based on this research, the scan rate affected the oxidation peak of potential, where the histamine potential (E) was moved to a positive course. A satisfactory equation (Figure 5b) was obtained between the scan rate inverse or symbolized as (1n v) and the peak potential

3.2.

3.3. Influence of pH

Based on this study, the heights and shapes of the histamine signal were affected by the pH value. The choice of pH level is a compulsory and imperative parameter that should be noted due to the fact that it can affect histamine redox. Several pH values were employed in order to observe the effect of pH at 0.25 mmol·L–1 of histamine using the CV technique, and pH ranged at 6.0–8.0 using 0.1 mol·L–1 PBS. Cyclic voltammetry was employed and ranged at 0.00 to +1.50 V, with 0.05 V·s–1 as a scan rate (Figure 6).

Figure 6.

Figure 6

Influence of pH values of histamine (0.25 mmol·L–1) in PBS (0.1 mol·L–1).

The acquired results reveal the effect of pH values in phosphate buffer solution. The connection between pH and peak potential of the supporting electrolyte is revealed in 6 and represented by using eq 5:

3.3. 5

Here, 0.7206 V/pH (slope) indicates that there is an electrode reaction between protons and electrons.28 The signal of histamine increased with pH ranging at 6.0–7.5 and then decreased at higher values (Figure 6).

The analytical response of histamine analysis was satisfactory when the application of pH values at 6.5–7.5 was applied. Nevertheless, the PBS (0.1 mol·L–1) at pH 7.5 was selected owing to the better anodic peak current acquired. Furthermore, with a substantial anodic peak with pH 7 and pH 7.5, it can be concluded that there is a reaction between the modified electrode and histamine imidazole ring. The imidazole ring of histamine contains pKa at 6.04, and thus the reaction between the electrode and histamine imidazole ring is gradually decreased because the pH is 8 or higher.

3.4. Electrochemical Behavior of Histamine on Unmodified SPE and PU-SPE-LiClO4

The sensitivity and selectivity of PU-SPE-LiClO4 and unmodified SPE are studied and compared in Figure 7. Histamine (1.0 mmol·L–1) was detected using the modified electrode, and the CV technique was used and ranged at 0.0 to +1.0 V (0.05 V·s–1 scan rate). The analytical responses of histamine were obtained and investigated on PU-SPE-LiClO4 and unmodified SPE.

Figure 7.

Figure 7

Cyclic voltammogram comparison between (a) SPE-PU-LiClO4 and (b) unmodified SPE to analyze histamine (1 mmol·L–1) in PBS (0.1 mol·L–1) at pH 7.5.

The voltammogram of the PU-SPE-LiClO4 released different redox couples with the unmodified SPE. Figure 7 shows a satisfactory oxidative peak of histamine that emerged at +0.31 V for the SPE-PU-LiClO4, and no cathodic peak was found, which can indicate that this was an irreversible reaction. Meanwhile, the unmodified SPE signal released an oxidative peak at +0.58 V and it can be deduced that there was no possibility for histamine to entrap or react on the SPE surface whether by physical or chemical adsorption.

Various studies have reported that the application of different voltammetries and electrodes that have been modified chemically or biologically will affect the electrode’s ability to analyze histamine and give different signals. A study reported that the application of the amperometry technique using a carbon electrode to analyze histamine released an anodic peak at +1.1 V.34 Meanwhile, the different results were provided by another study when the DPV was applied and the carbon paste electrode (CPE) was used as the electrode, determining an oxidative peak of histamine at +1.30 V, while for a CPE modified using a single-walled carbon nanotube (SWCNT), the histamine anodic peak was found at +1.20 V.28 Furthermore, the application of CPE modified by lignin showed an identical result at +1.20 V.33 Nevertheless, the application of SPE modified by PU-LiClO4 revealed a distinct anodic peak compared to other studies. Keow et al. (2007) studied and published the SPE application to analyze histamine in prawns, where according to their study, the SPE itself can be used to analyze histamine, so the electrode was modified using a photocuring method to produce a membrane to entrap enzyme immobilization and coat on the SPE surface. A satisfactory oxidative peak of this study emerged at +0.35 V and the identical result compared to this study.35

The histamine oxidation that can actually take place at the unmodified and modified electrode (−N=O) is one of the oxidation products after amines (−NH2) are oxidized.34 Nevertheless, a study reported that the −CH2–NH2 of histamine can lose 4H+ and form a (CN). Deamination of histamine can occur by the addition of specific enzymes such as horseradish peroxide and diamine oxidase.36 The application of silver oxide during electro-analysis can also oxidize several amines and cause the loss of carbon dioxide. Nevertheless, this technique is time-consuming and requires high temperatures.

PU-SPE-LiClO4 revealed that a particular signal of histamine contrasted to the unmodified SPE. The properties of PU cause it to react with the histamine. The amount of PU was studied in order to observe the analytical response during histamine analysis such as when 0.1, 0.3, 0.5, and 1 mg of polyurethane were applied. The study revealed that 0.1 mg of PU gave the optimum signal. Meanwhile, the other amounts of polyurethane gradually reduced the signal. Furthermore, in order to modify the electrode, several studies have considered the application of a thin polymer film in order to obtain the electron transfer among the analyte and the SPE surface.

The SPE modification using PU is possible due to the fact that PU can be recommended as a compatible film for adsorption purposes. Several studies have reported the benefit of PU when used to modify electrodes such as being able to control the pore size easily, being a very stable polymer, and being able to produce polymer on a large scale with low cost. Furthermore, a liquid substance can be entrapped by a physical technique into the polyurethane pore or can be entrapped by a chemical reaction.37 Histamine was entrapped inside the PU pore in this study by physical adsorption. The amine (−NH) group of histamine cannot react to the isocyanate (−NCO) groups of PU during the physical attachment of the histamine to PU. Thus, according to Puthongkham et al., this process is quite compatible with the electrochemical sensor using the voltammetry technique due to the fact that oxidation in histamine can be done.34 The obtained result of histamine (1 mmol·L–1) in PBS (0.1 mol·L–1) at pH 7.5 using 0.1 mg of PU film is presented in Figure 7 after being analyzed by the CV technique. It can be seen that there were no anodic and cathodic peaks of histamine when analyzed by SPEs. Furthermore, for the next study, we applied 0.1 mg of polyurethane in order to analyze histamine.

3.5. Analytical Performance

The DPV approach was employed in this research due to its modesty, sensitivity, and selectivity contrasted to CV. Thus, this technique was used to study the analytical response of histamine oxidation during analysis with the modified electrode. After doing several validation methods in terms of the pulse amplitude, scan rate, and pulse time, the DPV technique applied 50 mV·s–1 as a scan rate, 100 mV as the pulse amplitude, and 25 ms as a pulse time for further experiments. Table 1 presents several studies of histamine detection.

Table 1. Several Studies of Histamine Detection Using Electrochemical Sensors and Biosensors.

electrode technique LoD (mmol·L–1) linear range (mmol·L–1) references
diamine oxidase/carbon paste amperometry 3.5 0.1–325.9 Keow et al.35
amine oxidase/screen-printed carbon FIA/amperometry 3.0 10–300 Telsnig et al.38
amine oxidase/horseradish peroxidase/carbon chronoamperometry 0.18 0.4–2.4 Alonso-Lomillo et al.39
MWCNT/glassy carbon electrode DPV 0.076 0.1–100 Geto et al.40
pyrroloquinoline-Quinone-modified GCE amperometry 341 360–1530 Young et al.41
lignin-modified GCE SWV 0.28 5–200 Degefu et al.33
SPE-PU-LiClO4 CV and DPV 0.035 0.015–1 this research

3.6. Linearity

Several concentrations of histamine were applied and investigated using the DPV technique with the proposed technique, and the obtained voltammograms are shown in Figure 8.

Figure 8.

Figure 8

DP voltammograms of various histamine levels in PBS (0.1 mol·L–1) at pH 7.5 on SPE-PU-LiClO4.

The acquired results showed a direct proportionality regarding histamine levels ranging at 0.015–1 mmol·L–1. Using this data, this study was validated, and the data is shown in Table 2. The calibration curve was established and is shown in Figure 9, revealing the histamine in various levels in PBS (0.1 mol·L–1) at pH 7.5 using the SPE-PU-LiClO4. The line and points obtained were representatives for the value of the correlation coefficient and standard deviations. The relative standard deviation (RSD) was quite satisfactory, below 9% for six replicate analyses of each concentration.

Table 2. Validation Study of Histamine Detection Using DPV in PBS (0.1 mol·L–1) at pH 7.5 on the SPE-PU-LiClO4.

validation applied value
potential applied (E) +0.31 V
linear range (mmol·L–1) 0.015–1
coefficient correlation (R2) 0.9993
intraday (RSD, %) 3.05
interday (RSD, %) 9.02
detection limit (mmol·L–1) 0.035
quantitation limit (mmol·L–1) 0.105

Figure 9.

Figure 9

Calibration curve of various histamine levels ranging from 0.015 to 1 mmol·L–1.

3.7. Limits of Detection and Quantitation

The limit of detection (LoD) and limit of quantitation (LoQ) were calculated using the equation of (3.3·Sa/b) and (10·Sa/b), respectively. Sa represents the standard deviation of the intercept, while b represents the slope of the calibration curve for the LoD concentration ranging from 0.015 to 1 mmol·L–1. The calculated LoD and LoQ were 0.035 and 0.105 mmol·L–1 for histamine, respectively.

3.8. Precision and Stability

The study of precision and stability in this study indicated that SPE-PU- LiClO4 application is not suggested after the 7th day due to the fact that the signal will reduce for each day; nevertheless, the selectivity is steady. SPE-PU-LiClO4 was studied in terms of stability by calculating the oxidative peak of histamine standard at 0.13 mmol·L–1. The evaluation and determination were done from the 1st day until the 20th day for each week by using an identical electrode that can be kept in a droughty place to obtain a steady SPE-PU-LiClO4 (Figure 10).

Figure 10.

Figure 10

DPV voltammograms of histamine in PBS (0.1 mol·L–1) at pH 7.5 on SPE-PU-LiClO4 on different days starting from day 1 until day 28, and analysis was applied each week. (a) Analysis for day 1, (b) analysis for day 7, (c) analysis for day 14, (d) analysis for day 21, and (e) analysis for day 28.

The obtained results revealed that the histamine signal was decreased from 198.25 to 176.49 μA, presenting a 10.97% distinction in analytical response on the 7th day contrasted to the oxidative peak value of the 1st day; however, the potential applied did not shift. Furthermore, the 28th day showed a 47.4% of reduction in current response compared to the first day. Thus, it can be deduced that the peak was gradually decreased and it confirms that the polyurethane-LiClO4 modified electrode can be used for 1 week owing to the SPE-PU-LiClO4 sensitivity being reduced day by day and the application must be evaded so the bias calculation of histamine level in real samples can be avoided.

Histamine (0.01 mmol·L–1) was analyzed and employed to investigate the reliability of SPE-PU-LiClO4 during electro-analysis using the proposed method yet using different electrodes the similar surface area. Meanwhile, the precision of this technique was investigated in terms of intra- and interday investigations. The study of intraday was performed at two concentrations of histamine (0.1 and 0.01 mmol·L–1) by six repetition analyses. The analysis was acceptable after the RSD was acquired at 3.05%. Meanwhile, the study of interday was performed by using the identical histamine level (0.1 mmol·L–1) and using the identical modified electrode, and detection was done each day. The RSDs were acquired at 7.54 and 9.02% at levels 0.1 and 0.01 mmol·L–1 of histamine, respectively, indicating the better approach of histamine analysis by the proposed method. Thus, it denoted that the production and histamine detection using SPE-PU- LiClO4 are quite reproducible and reliable.

3.9. Disturbances

The selectivity and sensitivity of the proposed method and the presence of several amines such as putrescine and cadaverine represented biogenic amines and several amines according to their carbon number bonded directly to the nitrogen atom such as aniline, xanthine, and hexamine as primary, secondary, and tertiary amines, respectively. All of them were investigated using histamine analytical signals as well.

Various amines were analyzed using the DPV technique that contained histamine at 1 mmol·L–1, and the other amines were analyzed at 1 and 2 mmol·L–1. Based on the voltammogram, it can be deduced that all amines applied in this study did interfere with the histamine signal. The obtained result of the peak height of amines applied in this study can be denied. Furthermore, putrescine and cadaverine did not affect the histamine signal because they emerged at different potentials to histamine. Even aniline emerged at +0.43 V (Figure 11), which is a primary amine, and it concluded no disturbances in the histamine signal. Meanwhile, other biogenic amines such as cadaverine and putrescine that are generally found in fish accompanied by histamine, satisfactory anodic peaks of them were found at +0.18 and +0.19, respectively (Figure 11), practically not provoking the anodic peak of histamine. Furthermore, hexamine and xanthine did not affect the analytical response of the histamine signal when they were analyzed at 1 and 2 mmol·L–1, respectively.

Figure 11.

Figure 11

DP voltammograms of histamine (1 mmol·L–1) and the presence of other amines: (a) 1 mmol·L–1 of aniline, cadaverine, and putrescine and (b) 2 mmol·L–1 of aniline, cadaverine, and putrescine, respectively.

3.10. Implementation of the Developed and Validated Technique

The proposed method was applied for histamine analysis in real samples such as fish and canned mackerel. The fish sample was detected in six replicates. The development of histamine standard calibration was applied to determine the histamine concentration in mackerel quantitatively. Histamine was found in fish and canned samples. The histamine levels were found to be 17 μmol·L–1 (1.89 ppm) and 5.3 μmol·L–1 (0.59 ppm), respectively. The recovery study (accuracy) was studied using two histamine levels (0.1 and 0.01 mmol·L–1). The recoveries ranged from 94 to 103%, showing great accuracy. Furthermore, according to the regulation of the FDA, the fish samples analyzed in this study have no capability to poison during human consumption. In order to verify the detection in real samples, the performance was compared to other studies in terms of linear range and detection limit.

4. Conclusions

The research studies the electrochemical method validated and developed for the determination of histamine using SPE-PU-LiClO4. The PU film applied in this research has pores that can entrap histamine inside it. Furthermore, histamine exhibits not only an anodic peak at specific potential but also an irreversible reaction during analysis using a polyurethane-LiClO4 modified electrode. A satisfactory LoD and LoQ were also obtained in concentrations ranging at 0.015–1 mmol·L–1. Furthermore, the modesty of SPE-PU-LiClO4 production and deposition onto the surface electrode causing good accuracy was obtained, having a potential to detect histamine in real samples. Furthermore, the addition of LiClO4 into polyurethane improved the electro-analytical response of SPEs. PU has also the ability to adsorb histamine into its pores, causing histamine to release an oxidative peak compared to the unmodified SPE. Most of the common interfering compounds such as cadaverine and putrescine did not disturb the histamine signal. The validated method was demonstrated by analyzing histamine in fish mackerel and its product obtaining good accuracy with satisfactory RSD. The obtained results show that the validated DPV method proposes a great prospect for histamine detection as quality control of foods and beverages.

Acknowledgments

The authors wish to thank Alma Ata University for providing financial support. The work was also supported by the Department of Chemical Sciences, Universiti Kebangsaan Malaysia (UKM) for providing research facilities and financial support through its project grant no. GGP2019-021. The Analysis and Testing Center of CRIM is also acknowledged for its analytical and testing assistance.

The authors declare no competing financial interest.

References

  1. Liu Y.; Han F.; Liu Y.; Wang W. Determination of biogenic amines in wine using modified liquid-liquid extraction with high-performance liquid chromatography-fluorescence detector. Food Anal. Methods. 2020, 13, 911–922. 10.1007/s12161-020-01710-w. [DOI] [Google Scholar]
  2. Alsulami S.; Aji A. S.; Ariyasra U.; Sari S. R.; Tasrif N.; Yani F. F.; Lovegrove J. A.; Sudji I. R.; Lipoeto N. I.; Vimaleswaran K. S. Interaction between the genetic risk score and dietary protein intake on cardiometabolic traits in Southeast Asian. Genes Nutr. 2020, 15, 1–10. 10.1186/s12263-020-00678-w. [DOI] [PMC free article] [PubMed] [Google Scholar]
  3. Angulo M. F.; Flores M.; Aranda M.; Henriquez-Aedo K. Fast and selective method for biogenic amines determination in wines and beers by ultra high–performance liquid chromatography. Food Chem. 2020, 309, 125689. 10.1016/j.foodchem.2019.125689. [DOI] [PubMed] [Google Scholar]
  4. Nurwanti E.; Hadi H.; Chang J. S.; Chao J. C. J.; Paramashanti B. A.; Gittelsohn J.; Bai C. H. Rural-urban differences in dietary behavior and obesity: Results of the riskesdas study in 10-18-year-old Indonesian children and adolescents. Nutrients 2020, 11, 2813–2826. [DOI] [PMC free article] [PubMed] [Google Scholar]
  5. Munir M. A.; Inayatullah A.; Badrul H. A. Fish analysis containing biogenic amines using gas chromatography flame ionization detector. Sci. Technol. Indones. 2021, 6, 1–7. 10.26554/sti.2021.6.1.1-7. [DOI] [Google Scholar]
  6. Munir M. A.; Mackeen M. M. M.; Heng L. Y.; Badri K. H. Study of histamine detection using liquid chromatography and gas chromatography. ASM Sci. J. 2021, 16, 1–9. 10.32802/asmscj.2021.809. [DOI] [Google Scholar]
  7. Bogdanovic T.; Petricevic S.; Brkljaca M.; Listes I.; Pleadin J. Biogenic amines in selected foods as animal origin obtained from the Croatian retail market. Food Addit. Contam. A. 2020, 37, 815–830. 10.1080/19440049.2020.1726503. [DOI] [PubMed] [Google Scholar]
  8. Plakidi E. S.; Maragou N. C.; Dasenaki M. E.; Megoulas N. C.; Koupapris M. A.; Thomaidis N. S. Liquid chromatographic determination of biogenic amines in fish based on pyrene sulfonyl chloride pre-column derivatization. Foods 2020, 9, 609–629. 10.3390/foods9050609. [DOI] [PMC free article] [PubMed] [Google Scholar]
  9. Zhang W.; Wang X.; Yang S.; Niu Q.; Wu L.; Li Y.; Zhou J. Simultaneous quantification of five biogenic amines based on LC-MS/MS and its application in honeybee venom from different subspecies. Biomed. Chromatogr. 2020, 34, 4740. 10.1002/bmc.4740. [DOI] [PubMed] [Google Scholar]
  10. Munir M. A.; Badri K. H. The importance of derivatizing reagent in chromatography applications for biogenic amine detection in food and beverages. J. Anal. Chem. 2020, 2020, 5814389. 10.1155/2020/5814389. [DOI] [PMC free article] [PubMed] [Google Scholar]
  11. Papageorgiou M.; Lambropoulou D.; Morrison C.; Namieśnik J.; Plotka-Wasylka J. Direct solid-phase microextraction combined with gas chromatography-mass spectrometry for the determination of biogenic amines in wine. Talanta 2018, 183, 276–282. 10.1016/j.talanta.2018.02.006. [DOI] [PubMed] [Google Scholar]
  12. Ho L. S. J.; Fogel R.; Limson J. L. Generation and screening of histamine–specific aptamers for application in a novel impedimetric aptamer-based sensor. Talanta 2020, 208, 120474. 10.1016/j.talanta.2019.120474. [DOI] [PubMed] [Google Scholar]
  13. Kaçar C.; Erden P. E.; Dalkiran B.; Inal E. K.; Kiliç E. Amperometric biogenic amine biosensors based on Prussian blue, indium tin oxide nanoparticles, and diamine oxidase-or monoamine oxidase-modified electrodes. Anal. Bioanal. Chem. 2020, 412, 1933–1946. 10.1007/s00216-020-02448-4. [DOI] [PubMed] [Google Scholar]
  14. Raymundo-Pereira P. A.; Gomes N. O.; Shimizu F. M.; Machado S. A. S.; Oliveira O. N. Jr. Selective and sensitive multiplexed detection of pesticides in food samples using wearable, flexible glove-embedded non-enzymatic sensors. Chem. Eng. J. 2021, 408, 127279. 10.1016/j.cej.2020.127279. [DOI] [Google Scholar]
  15. Verma N.; Hooda V.; Gahlaut A.; Gothwal A.; Hooda V. Enzymatic biosensors for the quantification of biogenic amines: A literature update. Crit. Rev. Biotechnol. 2020, 40, 1–14. 10.1080/07388551.2019.1680600. [DOI] [PubMed] [Google Scholar]
  16. Akhoundian M.; Rüter A.; Shinde S. Ultratrace detection of histamine using a molecularly-imprinted polymer-based voltammetric sensor. Sensors 2017, 17, 645–654. 10.3390/s17030645. [DOI] [PMC free article] [PubMed] [Google Scholar]
  17. Raymundo-Pereira P. A.; Gomes N. O.; Machado S. A. S.; Oliveira O. N. Jr. Simultaneous, ultrasensitive detection of hydroquinone, paracetamol, and estradiol for quality control of tap water with a simple electrochemical method. J. Electroanal. Chem. 2019, 848, 113319. 10.1016/j.jelechem.2019.113319. [DOI] [Google Scholar]
  18. Nakthong P.; Kondo T.; Chailapakul O.; Siangproh W. Development of an unmodified screen-printed graphene electrode for nonenzymatic histamine detection. Anal. Methods 2020, 12, 5407–5414. 10.1039/D0AY01443E. [DOI] [PubMed] [Google Scholar]
  19. Baig N.; Sajid M.; Saleh T. A. Recent trends in nanomaterial-modified electrodes for electroanalytical applications. TrAC, Trends Anal. Chem. 2019, 111, 47–61. 10.1016/j.trac.2018.11.044. [DOI] [Google Scholar]
  20. Naureen B.; Haseeb A. S. M. A.; Basirun W. J.; Muhamad F. Recent advances in tissue engineering scaffolds based on polyurethane and modified polyurethane. Mater. Sci. Eng. C. 2021, 118, 111228. 10.1016/j.msec.2020.111228. [DOI] [PubMed] [Google Scholar]
  21. Losaria P. M.; Yim J. H. Enhancement of strain–sensing performance through gas-phase incorporation of siloxane into thermoplastic polyurethane–conducting polymer composite. Macromol. Chem. Phys. 2020, 221, 1–9. 10.1002/macp.202000155. [DOI] [Google Scholar]
  22. Gahlout P.; Choudhary V. EMI shielding response of polypyrrole-MWCNT/polyurethane composites. Synth. Met. 2020, 266, 116414. 10.1016/j.synthmet.2020.116414. [DOI] [Google Scholar]
  23. El-Nour K. M. A.; Salam E. T. A.; Soliman H. M.; Orabi A. S. Gold nanoparticles as a direct and rapid sensor for sensitive analytical detection of biogenic amines. Nanoscale Res. Lett. 2017, 12, 231–241. 10.1186/s11671-017-2014-z. [DOI] [PMC free article] [PubMed] [Google Scholar]
  24. Roales J.; Pedrosa J. M.; Guillen M. G.; Lopes-Costa T.; Pinto S. M. A.; Calvete M. J. F.; Pereira M. M. Optical detection of amine vapors using ZnTriad porphyrin thin films. Sens. Actuators B 2015, 210, 28–35. 10.1016/j.snb.2014.12.080. [DOI] [Google Scholar]
  25. de Lira F. R.; de Oliveira R. S. R.; da Silva J. H.; da Silva D. R.; Cavalcante M. G. Synthesis of a solid polymer electrolyte in the form of a self–sustainable membrane: sodium alginate and lithium perchlorate. J. Therm. Anal. Calorim. 2021, 1–17. 10.1007/s10973-021-10887-z. [DOI] [Google Scholar]
  26. Brza M.; Aziz S. B.; Saeed S. R.; Hamsan M. H.; Majid S. R.; Abdulwahid R. T.; Kadir M. F.; Abdullah R. M. Energy storage behavior of lithium-ion conducting poly (vinyl alcohol) (PVA): Chitosan (CS)-based polymer blend electrolyte membranes: Preparation, equivalent circuit modeling, ion transport parameters, and dielectric properties. Membranes 2020, 10, 381–400. 10.3390/membranes10120381. [DOI] [PMC free article] [PubMed] [Google Scholar]
  27. Badri K. H.; Ahmad S. H.; Zakaria S. Production of a high-functionality RBD palm kernel oil-based polyester polyol. J. Appl. Polym. Sci. 2001, 81, 384–389. 10.1002/app.1449. [DOI] [Google Scholar]
  28. Stojanović Z. S.; Mehmeti E.; Kalcher K.; Guzsvány V.; Stankovic D. M. SWCNT-modified carbon paste electrode as an electrochemical sensor for histamine determination in alcoholic beverages. Food Anal. Methods 2016, 9, 2701–2710. 10.1007/s12161-016-0452-3. [DOI] [Google Scholar]
  29. Butwong N.; Khajonklin J.; Thongbor A.; Luong J. H. T. Electrochemical sensing of histamine using a glassy carbon electrode modified with multiwalled carbon nanotubes decorated with Ag-Ag2O nanoparticles. Microchim. Acta 2019, 186, 714–723. 10.1007/s00604-019-3860-4. [DOI] [PubMed] [Google Scholar]
  30. Ahmad A.; Rahman M. Y. A.; Su’ait M. S. Morphological, infrared, and ionic conductivity studies of PEO-MG9-LiClO4 based solid polymer electrolyte. J. Appl. Polym. Sci. 2012, 124, 4222–4229. 10.1002/app.35403. [DOI] [Google Scholar]
  31. El-Raheem H. A.; Hassan R. Y. A.; Khaled R.; Farghali A.; El-Sherbiny I. M. Polyurethane-doped platinum nanoparticles modified carbon paste electrode for the sensitive and selective voltammetric determination of free copper ions in biological samples. Microchem. J. 2020, 155, 104765. 10.1016/j.microc.2020.104765. [DOI] [Google Scholar]
  32. Koita D.; Tzedakis T.; Kane C.; Diaw M.; Sock O.; Lavedan P. Study of the histamine electrochemical oxidation catalyzed by nickel sulfate. Electroanalysis 2014, 26, 2224–2236. 10.1002/elan.201400155. [DOI] [Google Scholar]
  33. Degefu H.; Amare M.; Tessema M.; Admassie S. Lignin modified glassy carbon electrode for the electrochemical determination of histamine in human urine and wine samples. Electrochim. Acta 2014, 121, 307–314. 10.1016/j.electacta.2013.12.133. [DOI] [Google Scholar]
  34. Puthongkham P.; Lee S. T.; Venton B. J. Mechanism of histamine oxidation and electropolymerization at carbon electrodes. Anal. Chem. 2019, 91, 8366–8373. 10.1021/acs.analchem.9b01178. [DOI] [PMC free article] [PubMed] [Google Scholar]
  35. Keow C. M.; Bakar F. A.; Salleh A. B.; Heng L. Y.; Wagiran R.; Bean L. S. An amperometric biosensor for the rapid assessment of histamine level in tiger prawn (Peneaeus monodon) spoilage. Food Chem. 2007, 105, 1636–1641. 10.1016/j.foodchem.2007.04.027. [DOI] [Google Scholar]
  36. Bulushi I. A.; Poole S.; Deeth H. C.; Dykes G. A. Biogenic amines in fish: Roles in intoxication, spoilage, and nitrosamine formation-A review. Crit. Rev. Food. Sci. Nutr. 2009, 49, 369–377. 10.1080/10408390802067514. [DOI] [PubMed] [Google Scholar]
  37. Kochanė T.; Budrienė S.; Pielchowski K.; Pielchowski J. Application of polyurethane-based materials for immobilization of enzymes and cells: A review. Chemija 2006, 17, 74–89. [Google Scholar]
  38. Telsnig D.; Kalcher K.; Leitner A.; Ortner A. Design of an amperometric biosensor for the determination of biogenic amines using screen-printed carbon working electrodes. Electroanalysis 2013, 25, 47–50. 10.1002/elan.201200378. [DOI] [Google Scholar]
  39. Alonso-Lomillo M. A.; Domínguez-Renedo O.; Matos P.; Arcos-Martínez M. J. Disposable biosensors for the determination of biogenic amines. Anal. Chim. Acta 2010, 665, 26–31. 10.1016/j.aca.2010.03.012. [DOI] [PubMed] [Google Scholar]
  40. Geto A.; Tessema M.; Admassie S. Determination of histamine in fish muscle at multi-walled carbon nanotubes coated conducting polymer modified glassy carbon electrode. Synth. Metals 2014, 191, 135–140. 10.1016/j.synthmet.2014.03.005. [DOI] [Google Scholar]
  41. Young J. A.; Jiang X.; Kirchhoff J. R. Amperometric Detection of histamine with a pyrroloquinoline – quinone modified electrode. Electroanalysis 2013, 25, 1589–1593. 10.1002/elan.201300114. [DOI] [Google Scholar]

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