A Biosensor for Simultaneous Detection of Epinephrine and Ascorbic Acid Based on Fe(III)–Polyhistidine-Functionalized Multi-Wall Carbon Nanotube Composites

Epinephrine (EP) is a very important chemical transmitter in the transmission of nerve impulses in the central nervous system of mammals. Ascorbic acid (AA) is considered to be the most important extracellular fluid antioxidant and has important antioxidant properties in the cell. In this study, a series of transition metal–polyhistidine-carboxylated multi-wall carbon nanotube nanocomposites were synthesized, and their simultaneous catalytic effects on epinephrine and ascorbic acid were investigated. The results showed that nanocomposites based on iron ions had the highest catalytic activity. The prepared biosensor expressed high selectivity toward EP and AA with LOD values of 0.1 μΜ (AA) and 0.01 μΜ (EP), and sensitivity values of 4.18 μA mM−1 with a range of 0.001–5 mM (AA), 50.98 μA mM−1 with a range of 0.2–100 μM (EP), and 265.75 μA mM−1 with a range of 0.1–1.0 mM (EP). Moreover, it showed good stability, good repeatability and high selectivity in real sample detection. This work is a reference for the design of new electrochemical enzyme-free biosensors and the detection of biomarkers.


Introduction
Epinephrine (EP) is a hormone and neurotransmitter synthesized and released by chrome cells in the adrenal medulla.It is an extremely important chemical transmitter in the central nervous system of mammals for transmitting nerve impulses and is nicknamed the "fight or flight" hormone.It is released into the blood system in response to excitement, fear, anger and other stimuli to raise blood sugar levels.Clinically, epinephrine is often used to treat cardiac arrest, anaphylactic shock and bronchial asthma [1,2].Studies have shown that epinephrine can induce the apoptosis of cardiomyocytes, nerve cells and coronary endothelial cells by regulating FAS-FASL-mediated apoptosis and activating the caspase-3 signaling pathway under pathological conditions [3].On the other hand, epinephrine can improve the level of basic metabolism as well as promote glycolysis, protein decomposition and fatty acid oxidation, which can trigger the body's oxidative stress response under special conditions, leading to the occurrence and development of certain diseases, and chemical transmitters such as EP can activate certain tumor adrenergic receptor-related signal transduction pathways.It plays a certain role in the process of tumor occurrence and development [4].
Oxidative stress has long been believed to be a negative effect caused by free radicals in the body and is related to aging and diseases.There are two kinds of antioxidant systems in response to oxidative stress: one is the enzyme antioxidant system, which includes catalase and superoxide dismutase; the other is a type of non-enzymatic antioxidant system that mainly includes reducing some physiologically active substances, such as ascorbic acid (vitamin C, L-ascorbic acid, AA), vitamin E and glutathione.Among many antioxidant substances, ascorbic acid is considered to be the most important extracellular liquid antioxidant and also has important antioxidant properties in the cell, which can effectively remove OH•, H 2 O 2 , etc.When the human body is exposed to an environment that can cause oxidative damage, such as excessive fatigue, ultraviolet radiation, and smoking, ascorbic acid becomes the first line of defense of antioxidants in the blood [5,6].
Both epinephrine and ascorbic acid have strong reducibility, but they play diametrically opposite antagonistic roles in the body's oxidative stress response.Adrenalin acts as a signaling molecule that produces free radicals by promoting basal metabolic and aerobic processes; ascorbic acid acts as a basic antioxidant, constantly monitoring the production of excessive free radicals in order to clean up in time.For these two substances, a fast, convenient, cheap and efficient detection technology is of great significance in both basic research and clinical diagnosis.
The detection methods for epinephrine and ascorbic acid usually include high-performance liquid chromatography [7], mass spectrometry [8] and fluorescence spectrometry [9].These conventional detection methods have the disadvantages of expensive equipment, complicated operation, and specialized sample processing.In today's rapidly developing society, it is increasingly difficult to meet daily needs; therefore, a fast, cheap and efficient analysis and detection system is urgently required.As a new instrument and technical means, biosensors are attracting increasing attention.Epinephrine and ascorbic acid are generally present in biological samples at the same time.However, the oxidation potential of ascorbic acid on the surface of most solid electrodes is very close to that of epinephrine, which is prone to overlapping responses, so it is difficult to achieve the simultaneous detection of both.The usual solution is to eliminate ascorbic acid's interference with epinephrine [10] or to separate the chemical reactions [11,12].Hu et al. constructed a simple electrochemical sensor by modifying carbon nanotubes on the surface of glassy carbon electrodes.They used cyclic voltammetry to simultaneously detect epinephrine and ascorbic acid, and they observed the oxidation potential of negatively shifted ascorbic acid, thus realizing an effective distinction between the two [13].Sun et al. constructed a simple electrochemical sensor by synthesizing a layer of benzotriazole self-assembly film on the surface of a gold electrode, which effectively distinguished the oxidation potential of epinephrine and ascorbate, and the oxidation peak potential difference between the two was 200 ± 10 mV, thus realizing the simultaneous detection of both [14].
Since Japanese scientist Iijima [15] discovered carbon nanomaterials with a coaxial tubular structure-carbon nanotubes in 1991, carbon nanotubes (CNTs) have been characterized by their special nanostructures, excellent mechanical properties and electrical conductivity.They have been extensively researched and applied as biosensors [16,17], catalytic materials [18], energy storage materials [19], drug carriers [20], etc. Carbon nanotubes have excellent electrical conductivity, and their electron transfer efficiency is affected by the length of carbon nanotubes to a certain extent, and electron transfer is mainly carried out along the radial direction of carbon nanotubes rather than through the diameter of the tube [21].Compared with randomly distributed carbon nanotubes, carbon nanotubes microarrays, or aligned carbon nanotubes, it is possible to effectively avoid overlapping entanglement between carbon tubes due to their highly ordered parallel arrangement structure and reduced contact resistance [22].Therefore, short carbon nanotubes with an ordered structure have better electrical conductivity.Carboxylated multi-walled carbon nanotubes (CMWCNTs) arrays cut short and open by chemical oxidation have significant advantages in improving electron transport efficiency.In addition to the above highly ordered structures, the inner wall of CMWCNTs also participated in electron transport and had a large current-carrying capacity [23].At the same time, CMWCNTs also play a crucial role in improving the performance of biosensors.
Poly-L-histidine (PLH) is a multifunctional polyelectrolyte that can be used to modify CMWCNTs microarrays.PLH molecules contain the lipophilic π-π-conjugated aromatic functional group imidazolyl, so PLH can achieve non-covalent bonding with CMWCNTs through π-π stacking.At the same time, PLH can also achieve covalent cross-linking through the formation of amide bonds between its free amino group and the carboxyl group of CMWCNTs.Both π-π-conjugated electrons and lone pairs play an important role in the electron transport process [24,25].The imidazole group in the PLH side chain acts as a ligand that can chelate a variety of metal ions or atoms, and it can also achieve direct electron transfer to CMWCNTs.Therefore, the modification of PLH on the surface of CMWCNTs arrays can significantly enhance electron transport.In addition, it has been confirmed that metal ions (or atoms)-polyhistidine complexes have obvious catalytic effects on many substances.
In this study, a series of transition metal-polyhistidine-carboxylated multi-wall carbon nanotube nanocomposites were synthesized by chelating polyhistidine-imidazolyl to transition metal ions, and their simultaneous catalytic effects on epinephrine and ascorbic acid were investigated.The results showed that these nanocomposites could distinguish the oxidation potential of epinephrine and ascorbic acid effectively, and the nanocomposites based on iron ions had the highest catalytic activity.Therefore, in this study, nanocomposite materials based on iron ions were selected for the construction of a biosensing interface and the simultaneous detection of epinephrine and ascorbic acid.

Screening of Transition Metal Ions in Me-PLH-CMWCNTs Nanocomposites
In this study, cyclic voltammetry was used to investigate the electrocatalytic effects of a series of nanocomposite electrodes based on transition metal ions on epinephrine and ascorbic acid at the same time.The results are shown in Figure 1.On the surface of the bare gold electrode, both EP and AA showed characteristic REDOX peaks with a large EP oxidation peak near 250 mV and a pair of smaller REDOX peaks around −180 mV.The oxidation peak of AA appears near 100 mV.Due to the small difference in oxidation potential between the two, and the low response current of AA on the bare electrode surface, it is not easy to distinguish the interference from EP.The response of gold electrodes modified with CMWCNTs and PLH-CMWCNTs to EP and AA was significantly enhanced.According to the analysis described in the previous section, this was due to the increased electron transfer rate and specific surface area at the electrode interface promoted by CMWCNTs and PLH-CMWCNTs.The response of nanocomposites containing different transition metal ions to EP and AA was significantly improved, indicating that transition metal ions play an obvious role as catalysts in the electrocatalytic oxidation of the two substances.Among them, the effect of iron ion is the most significant.
In order to select the ion with the best catalytic effect, the electrocatalytic effect of the nanocomposite electrode based on the transition metal ion on EP and AA was investigated using the differential pulse method.The catalytic effect of this method is basically the same as that of cyclic voltammetry, in which the bare gold electrode has almost no response to AA, EP only has an oxidation peak near 150 mV, AA has an oxidation peak near −50 mV, and the oxidation potential difference between the two is larger and easier to distinguish than that of cyclic voltammetry.Figure 2 presents the oxidation peak current of different modified electrodes.It can be seen that among the eight transition metal ions, iron ion has the best catalytic effect.Therefore, iron ion was selected as the catalytic active center ion for the simultaneous detection of EP and AA in this study.In order to select the ion with the best catalytic effect, the electrocatalytic effect of the nanocomposite electrode based on the transition metal ion on EP and AA was investigated using the differential pulse method.The catalytic effect of this method is basically the same as that of cyclic voltammetry, in which the bare gold electrode has almost no response to AA, EP only has an oxidation peak near 150 mV, AA has an oxidation peak near −50 mV, and the oxidation potential difference between the two is larger and easier to distinguish than that of cyclic voltammetry.Figure 2 presents the oxidation peak current of different modified electrodes.It can be seen that among the eight transition metal ions, iron ion has the best catalytic effect.Therefore, iron ion was selected as the catalytic active center ion for the simultaneous detection of EP and AA in this study.

Morphological Characterization of Fe(III)-PLH-CMWCNTs
Firstly, the composite materials were characterized and analyzed.Figure 3 shows the FTIR spectra of each nanomaterial, in which the stretching vibration of carboxyl group is represented at 1000 cm −1 .Compared with curve a and curve b, it can be seen that the carboxyl absorption peak of CMWCNTs is significantly higher than that of MWCNTs,

Morphological Characterization of Fe(III)-PLH-CMWCNTs
Firstly, the composite materials were characterized and analyzed.Figure 3 shows the FTIR spectra of each nanomaterial, in which the stretching vibration of carboxyl group is represented at 1000 cm −1 .Compared with curve a and curve b, it can be seen that the carboxyl absorption peak of CMWCNTs is significantly higher than that of MWCNTs, indicating that CMWCNTs with a good carboxylation effect were obtained in this experiment.In curve c, 1623 cm −1 , 1608 cm −1 and 1536 cm −1 represent the stretching vibrations of C=O, C=N and C-N, respectively.Compared with curve b, the increase in absorption peaks at these positions is mainly attributed to the modification of PLH, which also indicates that PLH has been successfully modified to CMWCNTs.The peaks of the above characteristic peaks in curve d are significantly lower than those in curve c.The reason may be that the modification of iron ions interferes with the absorption of infrared light by these groups, which also indicates that iron ions have been chelated into the nanocomposites.Figure 4A shows the TEM image of CMWCNTs, in which the typical hollow tub structure of multi-walled carbon nanotubes and some carbon nanotubes cut shor mixed acid oxidation can be observed.Figure 4B shows the tube end enlargement of CWMCNTs segment.The multilayer graphite lamellar structure on the wall of the car nanotube and the opening of the tube end truncated by carboxylation can be cle observed.Figure 4C shows a typical PLH-modified CMWCNTs with closed tube e from which a PLH film about 2 nm thick on the outer side of the tube wall can be cle observed.Figure 4D   Figure 4A shows the TEM image of CMWCNTs, in which the typical hollow tubular structure of multi-walled carbon nanotubes and some carbon nanotubes cut short by mixed acid oxidation can be observed.Figure 4B shows the tube end enlargement of one CWMCNTs segment.The multilayer graphite lamellar structure on the wall of the carbon nanotube and the opening of the tube end truncated by carboxylation can be clearly observed.Figure 4C shows a typical PLH-modified CMWCNTs with closed tube ends, from which a PLH film about 2 nm thick on the outer side of the tube wall can be clearly observed.Figure 4D   Combining FTIR, TEM, XPS and EDX characterization, it is fully proved that Fe(III)-PLH-CMWCNTs nanocomposites have been successfully prepared in this study.

Electrochemical Activity of Fe(III)-PLH-CMWCNTs/AuE
The electrical conductivity of nanocomposites and the effective active area of gold electrodes modified with different materials were analyzed with cyclic voltammetry in a potassium ferricyanide system, and the results are shown in Figure 5.The electrodes modified with different materials showed a characteristic REDOX peak of [Fe(CN)6] 4−/3− in the potassium ferricyanide system, and the REDOX current of the gold electrode modified Combining FTIR, TEM, XPS and EDX characterization, it is fully proved that Fe(III)-PLH-CMWCNTs nanocomposites have been successfully prepared in this study.

Electrochemical Activity of Fe(III)-PLH-CMWCNTs/AuE
The electrical conductivity of nanocomposites and the effective active area of gold electrodes modified with different materials were analyzed with cyclic voltammetry in a potassium ferricyanide system, and the results are shown in Figure 5.The electrodes modified with different materials showed a characteristic REDOX peak of [Fe(CN) 6 ] 4−/3− in the potassium ferricyanide system, and the REDOX current of the gold electrode modified with CMWCNTs and PLH-CMWCNTs was significantly increased, indicating that the electrodes modified with CMWCNTs had good conductivity and a large specific surface area.PLH-CMWCNTs competitively bind iron ions in [Fe(CN) 6 ] 4−/3− due to the chelation of PLH side-chain imidazolyl.Therefore, although Fe ions are modified in Fe(III)-PLH-CMWCNTs, the conductivity of the potassium ferricyanide system does not improve.The relative surface area of the modified electrode is similar to that of the PLH-CMWCNTmodified electrode.The effective active area of different modified electrodes can be obtained using the Randles-Ševčík Equation (1) [26]: where i p stands for the peak current (µA); n represents the number of electron transfers in the REDOX reaction, which is 1; D represents the molecular diffusion coefficient in the solution, which is (6.70 ± 0.02) × 10 −6 cm 2 s −1 ; C 0 represents the concentration of probe molecules in the solution, that is, 10 mM; v represents the scanning rate, which is now 50 mV s −1 ; and A eff corresponds to the effective active area (cm 2 ) of the modified electrode.The effective active area of different modified electrodes can be obtained by substituting the peak oxidation current of each electrode in Figure 5 into the above equation.Among them, the effective active area of Fe(III)-PLH-CMWCNTs/AuE was 0.113 cm 2 , which is the same as that of PLH-CMWCNTs/AuE, and it is 1.6 and 1.2 times that of CMWCNTs/AuE and bare gold electrodes, respectively.We have reason to believe that it is the introduction of polyhistidine that significantly improves the electrical conductivity of the metal-organic nanocomposite and also determines the high sensitivity of the sensor constructed in this study.with CMWCNTs and PLH-CMWCNTs was significantly increased, indicating that the electrodes modified with CMWCNTs had good conductivity and a large specific surface area.PLH-CMWCNTs competitively bind iron ions in [Fe(CN)6] 4−/3− due to the chelation of PLH side-chain imidazolyl.Therefore, although Fe ions are modified in Fe(III)-PLH-CMWCNTs, the conductivity of the potassium ferricyanide system does not improve.The relative surface area of the modified electrode is similar to that of the PLH-CMWCNTmodified electrode.The effective active area of different modified electrodes can be obtained using the Randles-Ševčík Equation (1) [26]: where  stands for the peak current (μA); n represents the number of electron transfers in the REDOX reaction, which is 1; D represents the molecular diffusion coefficient in the solution, which is (6.70 ± 0.02) × 10 −6 cm 2 s −1 ; C0 represents the concentration of probe molecules in the solution, that is, 10 mM; v represents the scanning rate, which is now 50 mV s −1 ; and Aeff corresponds to the effective active area (cm 2 ) of the modified electrode.The effective active area of different modified electrodes can be obtained by substituting the peak oxidation current of each electrode in Figure 5 into the above equation.Among them, the effective active area of Fe(III)-PLH-CMWCNTs/AuE was 0.113 cm 2 , which is the same as that of PLH-CMWCNTs/AuE, and it is 1.6 and 1.2 times that of CMWCNTs/AuE and bare gold electrodes, respectively.We have reason to believe that it is the introduction of polyhistidine that significantly improves the electrical conductivity of the metal-organic nanocomposite and also determines the high sensitivity of the sensor constructed in this study.The electrocatalytic effects of Fe(III)-PLH-CMWCNTs/AuE on 1.0 mM AA and 0.5 mM EP in a 0.1 M PBS (pH 7.0) system were investigated using cyclic voltammetry.As shown in Figure 6, the electrocatalytic oxidation behaviors of AA and EP on different modified electrode surfaces are basically consistent with those discussed before.It was also observed that in the response of the bare gold electrode to AA and EP at this time, it is impossible to distinguish the oxidation peak of the two, mainly because on the surface The electrocatalytic effects of Fe(III)-PLH-CMWCNTs/AuE on 1.0 mM AA and 0.5 mM EP in a 0.1 M PBS (pH 7.0) system were investigated using cyclic voltammetry.As shown in Figure 6, the electrocatalytic oxidation behaviors of AA and EP on different modified electrode surfaces are basically consistent with those discussed before.It was also observed that in the response of the bare gold electrode to AA and EP at this time, it is impossible to distinguish the oxidation peak of the two, mainly because on the surface of the bare gold electrode, EP is prone to electropolymerization, so the electrode passivation, which also shows the necessity of using nanocomposite materials to modify the electrode, on the one hand, can effectively prevent EP electropolymerization, avoiding the loss of sensitivity of electrode passivation.On the other hand, it can effectively distinguish the oxidation potential of AA and EP and improve the catalytic effect.passivation, which also shows the necessity of using nanocomposite materials to mo the electrode, on the one hand, can effectively prevent EP electropolymerization, avoid the loss of sensitivity of electrode passivation.On the other hand, it can effecti distinguish the oxidation potential of AA and EP and improve the catalytic effect.The electrocatalytic behavior of Fe(III)-PLH-CMWCNTs/AuE on 1.0 mM AA and mM EP at different scanning rates was also investigated, and the results are show Figure 7.It can be seen from Figure 7A that the oxidation currents of both AA and gradually increase with the increase in scanning rate.The peak oxidation current of and EP (at 250 mV) is linearly fitted to the square root of the scanning rate, and it is fo that it presents a good linear relationship.The linear equations for AA and EP are Ip( = 0.01199C (AA) − 0.01854 (R 2 = 0.993) and Ip(EP) = 0.01141C (EP) − 0.00196 (R 2 = 0.9 respectively (as shown in Figure 7B).It is shown that the electrocatalytic oxidation of and EP at the sensor interface constructed in this study is a diffusion-controlled proc The slopes of the two were substituted into Equation (1), and according to the effec active area of Fe(III)-PLH-CMWCNTs/AuE (0.113 cm 2 ), the diffusion coefficient of was 1.94 × 10 −5 cm 2 s −1 and that of EP was 1.76 × 10 −5 cm 2 s −1 .These values are basic consistent with those previously reported (5.9 × 10 −5 cm 2 s −1 [27], 1.24 × 10 −5 cm 2 s −1 [28 The electrocatalytic behavior of Fe(III)-PLH-CMWCNTs/AuE on 1.0 mM AA and 0.5 mM EP at different scanning rates was also investigated, and the results are shown in Figure 7.It can be seen from Figure 7A that the oxidation currents of both AA and EP gradually increase with the increase in scanning rate.The peak oxidation current of AA and EP (at 250 mV) is linearly fitted to the square root of the scanning rate, and it is found that it presents a good linear relationship.The linear equations for AA and EP are Ip(AA) = 0.01199C (AA) − 0.01854 (R 2 = 0.993) and Ip(EP) = 0.01141C (EP) − 0.00196 (R 2 = 0.992), respectively (as shown in Figure 7B).It is shown that the electrocatalytic oxidation of AA and EP at the sensor interface constructed in this study is a diffusioncontrolled process.The slopes of the two were substituted into Equation (1), and according to the effective active area of Fe(III)-PLH-CMWCNTs/AuE (0.113 cm 2 ), the diffusion coefficient of AA was 1.94 × 10 −5 cm 2 s −1 and that of EP was 1.76 × 10 −5 cm 2 s −1 .These values are basically consistent with those previously reported (5.9 × 10 −5 cm 2 s −1 [27], 1.24 × 10 −5 cm 2 s −1 [28]).

Simultaneous Detection of AA and EP by Fe(III)-PLH-CMWCNTs/AuE
In this experiment, the simultaneous detection effect of Fe(III)-PLH-CMWCN on AA and EP in a 0.1 M PBS (pH 6.0) system was investigated using the differenti method, and the results are shown in Figure 8A.The oxidation potential of AA 50 mV, and the oxidation potential of EP is about 250 mV.At the same concentra oxidation current of EP is obviously higher than that of AA, but the oxidation pot EP shifts slightly to the right with the increase in the concentration of AA and EP may be caused by the slight change in pH value of the solution caused by the inc

Simultaneous Detection of AA and EP by Fe(III)-PLH-CMWCNTs/AuE
In this experiment, the simultaneous detection effect of Fe(III)-PLH-CMWCNTs/AuE on AA and EP in a 0.1 M PBS (pH 6.0) system was investigated using the differential pulse method, and the results are shown in Figure 8A.The oxidation potential of AA is about 50 mV, and the oxidation potential of EP is about 250 mV.At the same concentration, the oxidation current of EP is obviously higher than that of AA, but the oxidation potential of EP shifts slightly to the right with the increase in the concentration of AA and EP, which may be caused by the slight change in pH value of the solution caused by the increase in the concentration of AA and EP.The peak oxidation current and concentration of the two were linearly fitted, and the results are shown in Figure 8B,C.In the range of 0.001~5 mM, the oxidation current of AA showed a good linear relationship with the concentration.The regression equation was y AA (mA) = 0.00418x (mM) + 0.01944 (R 2 = 0.997), the sensitivity was 4.18 µA mM −1 , and the lowest detection limit was 0.1 µm (S/N = 3).The linear regression equation is y EP1 (mA) = 0.26575x (mM) + 0.00517 (R 2 = 0.996), and the sensitivity in this range is 265.75 µA mM −1 .In the concentration range of 0.1~1.0mM, the linear regression equation is y EP2 (mA) = 0.05098x (mM) + 0.02205 (R 2 = 0.998), the sensitivity in this range is 50.98 µA mM −1 and the sensor's lowest detection limit for EP is 0.01 µm (S/N = 3).
Int. J. Mol.Sci.2024, 25,7883 sensitivity in this range is 265.75 μA mm −1 .In the concentration range of 0.1~1.0m linear regression equation is yEP2 (mA) = 0.05098x (mM) + 0.02205 (R 2 = 0.99 sensitivity in this range is 50.98 μA mm −1 and the sensor's lowest detection limit fo 0.01 μm (S/N = 3).Table 1 compares the effects of Fe(III)-PLH-CMWCNTs/AuE and the prev reported sensors on the simultaneous detection of AA and EP.Compared wi minimum detection limit, detection range and sensitivity of each sensor, the bio Table 1 compares the effects of Fe(III)-PLH-CMWCNTs/AuE and the previously reported sensors on the simultaneous detection of AA and EP.Compared with the minimum detection limit, detection range and sensitivity of each sensor, the biosensor based on iron (III)-polyhistidine-functionalized multi-wall carbon nanotube nanocomposite materials constructed in this study showed a higher sensitivity, wider detection range and lower detection limit than most reported sensors.In summary, the biosensor constructed in this study showed excellent performance in terms of catalytic activity and sensitivity, which was mainly attributed to the high-efficiency electrocatalytic activity of Fe(III)-PLH in the metal-organic nanocomposite as the catalytic activity center.At the same time, PLH-CMWCNTs greatly improved the electron transfer efficiency at the biosensing interface, increased the effective active area, and ensured the enrichment of a large number of substances to be measured at the biosensing interface.

Reproducibility, Stability, Anti-Interference and Suitability Evaluation
Reproducibility is an important measure of a standard analytical method.The reproducibility of this study protocol was evaluated by using the same experimental procedure as above.Seven electrodes were prepared successively, and their electrochemical responses to 1.0 mM AA and 0.2 mM EP were investigated in a 0.1 M PBS (pH 6.0) system.The seven electrodes showed almost the same electrochemical response to AA and EP, and the standard deviation was 4.17%, indicating that the scheme had good reproducibility.The stability of the sensor constructed in this study was evaluated by examining the electrochemical response of 1.0 mM AA and 0.2 mM EP with the same electrode at an interval of 15 days.The results showed that the response current of the electrode to AA and EP could still reach 95.2% and 96.3% of the initial current after 90 days, indicating that the electrode had good stability.
In the testing of real samples, other electrophysiological active substances such as glucose (Glu), acetaminophen (AP), uric acid (UA) and some metal ions (K + , Na + , Ca 2+ , Zn 2+ , etc.) may interfere with the detection of AA and EP.The anti-interference performance of the sensor is evaluated by detecting its electrochemical response to 1.0 mM AA and 0.2 mM EP in the presence of the above interfering substances, and the results are shown in Figure 9.As can be seen from the figure, Glu has almost no response in the scanning range of −400~600 mV, which does not interfere with the sensor detection application.UA and AP had an oxidation peak around 400 mV and 420 mV, respectively, but AA and AP had almost no effect on the response.The sensor also shows good anti-jamming performance against common metal ions in some physiological samples.

Analysis in Real Samples
In this study, the applicability of the constructed sensor was investigated in the detection of real samples.AA samples were extracted from commercial vitamin tablets (0.1 g/tablet) with 0.1 M PBS (pH 6.0) solution grinding at a 1:1000 mass ratio.EP samples were obtained from the diluent of medical injection (content 1 mg/branch) and diluted with 0.1 M PBS (pH 6.0) solution at a 1:1000 volume ratio.The serum samples were diluted to 1% with 0.1 M PBS (pH 6.0) solution and centrifuged at 12,000 rpm for 30 min, and the supernatant was filtered using a 0.2 μm microporous filter membrane in three stages, stored at 4 °C and placed at room temperature before use.The test results of recoveries are shown in Table 2.The recoveries of AA and EP ranged from 96.38 to 106.84% and 94.93 to 104.45 %, respectively.The total standard deviations were 2.45~5.12%.The above data show that the sensor constructed in this study has practical applicability, and they provide a certain reference value for the daily detection and clinical diagnosis of AA and EP.

Analysis in Real Samples
In this study, the applicability of the constructed sensor was investigated in the detection of real samples.AA samples were extracted from commercial vitamin tablets (0.1 g/tablet) with 0.1 M PBS (pH 6.0) solution grinding at a 1:1000 mass ratio.EP samples were obtained from the diluent of medical injection (content 1 mg/branch) and diluted with 0.1 M PBS (pH 6.0) solution at a 1:1000 volume ratio.The serum samples were diluted to 1% with 0.1 M PBS (pH 6.0) solution and centrifuged at 12,000 rpm for 30 min, and the supernatant was filtered using a 0.2 µm microporous filter membrane in three stages, stored at 4 • C and placed at room temperature before use.The test results of recoveries are shown in Table 2.The recoveries of AA and EP ranged from 96.38 to 106.84% and 94.93 to 104.45 %, respectively.The total standard deviations were 2.45~5.12%.The above data show that the sensor constructed in this study has practical applicability, and they provide a certain reference value for the daily detection and clinical diagnosis of AA and EP.centrifugation process was repeated until the pH of the solution was close to neutral.The precipitate was dried at 85 • C under vacuum, producing the carboxylated multi-walled carbon nanotubes, which were denoted as CMWCNTs.

Preparation of PLH Functionalized CMWCNs
Then, a 0.1 M PBS (pH 6.0) suspension of CMWCNTs of 1 mL and 1 mg mL −1 was prepared and fully dispersed after ultrasonic treatment.Next, 2 mM EDC (the final reaction concentration is not specified below) and 5 mM NHS were added and reacted for 15 min at room temperature.At the end of the reaction, the EDC and NHS were quenched by adding 20 mM mercaptoethanol and centrifugally suspended on 1 mL 0.1 M PBS (pH 7.0) to obtain carboxyl-activated CMWCNTs.
Next, 1 mL and 1 mg mL −1 PLH 0.1 M HCl solution was prepared and added to the carboxyl-activated CMWCNTs suspension, reacted for 2 h under ultrasonic conditions, and centrifugally suspended in 1 mL of deionized water to obtain PLH-functionalized CMWCNTs.

Construction of the Sensing Interface of Me-PLH-CMWCNTs/AuE
A gold electrode was polished into a smooth mirror by using nanometer aluminum oxide powder with a diameter of 0.3 µm, 0.1 µm and 0.05 µm successively, and soaked in Piranha solution (30% HNO 3 :98% H 2 SO 4 = 1:3, v:v) at 90 • C for 10 min.Then, it was ultrasonically cleaned in deionized water and anhydrous ethanol alternately, 3 times for 2 min each time, and dried with high-purity nitrogen for use.
We took 10 µL of each metal-organic nanocomposite and applied it to the surface of the newly cleaned gold electrode, dried it at room temperature, and then used it for Me-PLH-CMWCNTs/AuE (Me = Fe (III), Co (II), Ni (II), Cu (II), zinc (II), Mn (II), Cd (II), and Pd (II)).The preparation process of Fe(III)-PLH-CMWCNTs/AuE is shown in Figure 10.centrifugally suspended in 1 mL of deionized water to obtain PLH-functionalized CMWCNTs.

Construction of the Sensing Interface of Me-PLH-CMWCNTs/AuE
A gold electrode was polished into a smooth mirror by using nanometer aluminum oxide powder with a diameter of 0.3 μm, 0.1 μm and 0.05 μm successively, and soaked in Piranha solution (30% HNO3:98% H2SO4 = 1:3, v:v) at 90 °C for 10 min.Then, it was ultrasonically cleaned in deionized water and anhydrous ethanol alternately, 3 times for 2 min each time, and dried with high-purity nitrogen for use.
We took 10 μL of each metal-organic nanocomposite and applied it to the surface of the newly cleaned gold electrode, dried it at room temperature, and then used it for Me-PLH-CMWCNTs/AuE (Me = Fe (III), Co (II), Ni (II), Cu (II), zinc (II), Mn (II), Cd (II), and Pd (II)).The preparation process of Fe(III)-PLH-CMWCNTs/AuE is shown in Figure 10.

Preparation of the Electrochemical System
Using a conventional three-electrode test system, Me-PLH-CMWCNTs/AuE was used as the working electrode, while a platinum wire (φ = 1 mm) was used as the counter electrode, and a saturated KCl-filled Ag/AgCl glass electrode was used as the reference electrode.The electrochemical catalytic performance of the prepared electrodes for

Preparation of the Electrochemical System
Using a conventional three-electrode test system, Me-PLH-CMWCNTs/AuE was used as the working electrode, while a platinum wire (φ = 1 mm) was used as the counter electrode, and a saturated KCl-filled Ag/AgCl glass electrode was used as the reference electrode.The electrochemical catalytic performance of the prepared electrodes for epinephrine and ascorbic acid in a 0.1 M PBS system was investigated using cyclic voltammetry, differential pulse voltammetry, and other electrochemical analysis methods.All electrochemical tests were conducted at room temperature.

Conclusions
In this study, polyhistidine, as a metal ligand, modified carboxylated multi-walled carbon nanotubes and further chelated iron ions, and it innovatively synthesized a metal-organic nanocomposite with high catalytic activity of both ascorbic acid and epinephrine.To our knowledge, this strategy is the first of its kind in the construction of biosensing interfaces.Polyhistidine is a multifunctional polyelectrolyte of polypeptides.Its side-chain functional group, imidazolyl, gives the polymer special conductivity and metal-chelation ability.By combining multi-walled carbon nanotubes, the electron transfer efficiency of the biosensing interface is greatly improved, and the effective active area of the sensing interface is significantly increased.Thus, the sensing interface can absorb more detection substrates, which fundamentally determines that the constructed sensor has higher sensitivity, a wider detection range, and a lower detection limit.The sensor also has good repeatability, stability, and anti-interference performance, and it has practical application value in real sample detection.

Data Availability Statement:
The original contributions presented in the study are included in the article/supplementary materials, further inquiries can be directed to the corresponding author/s.

Conflicts of Interest:
The authors declare no conflicts of interest.

Figure 2 .
Figure 2. Comparison of the oxide peak currents of a series of electrodes with different modifications toward 1 mM AA and 0.5 mM EP via differential pulse voltammetry.
Figure4Ashows the TEM image of CMWCNTs, in which the typical hollow tub structure of multi-walled carbon nanotubes and some carbon nanotubes cut shor mixed acid oxidation can be observed.Figure4Bshows the tube end enlargement of CWMCNTs segment.The multilayer graphite lamellar structure on the wall of the car nanotube and the opening of the tube end truncated by carboxylation can be cle observed.Figure4Cshows a typical PLH-modified CMWCNTs with closed tube e from which a PLH film about 2 nm thick on the outer side of the tube wall can be cle observed.Figure4Dshows the local high-angle toroidal dark field (HADDF) imag Fe(III)-PLH-CMWCNTs. EDX spectral analysis was performed on the region in the w box.The results are shown in Figure4E.Peak C in the spectrum came from CMWC and PLH, while peak N came from PLH.The elemental composition (wt%) of the Fe PLH-CMWCNTs shows 83.62% (C), 1.12% (N), 3.55% (O), 8.48% (Fe) and 3.23%(Cu).indicates that iron ions have been successfully chelated into the nanomaterial, and th peak in the figure is mainly from the copper microgate supporting film prepared by T
Figure4Ashows the TEM image of CMWCNTs, in which the typical hollow tubular structure of multi-walled carbon nanotubes and some carbon nanotubes cut short by mixed acid oxidation can be observed.Figure4Bshows the tube end enlargement of one CWMCNTs segment.The multilayer graphite lamellar structure on the wall of the carbon nanotube and the opening of the tube end truncated by carboxylation can be clearly observed.Figure4Cshows a typical PLH-modified CMWCNTs with closed tube ends, from which a PLH film about 2 nm thick on the outer side of the tube wall can be clearly observed.Figure4Dshows the local high-angle toroidal dark field (HADDF) image of Fe(III)-PLH-CMWCNTs. EDX spectral analysis was performed on the region in the white box.The results are shown in Figure4E.Peak C in the spectrum came from CMWCNTs and PLH, while peak N came from PLH.The elemental composition (wt%) of the Fe(III)-PLH-CMWCNTs shows 83.62% (C), 1.12% (N), 3.55% (O), 8.48% (Fe) and 3.23%(Cu).This

Figure 7 .
Figure 7. (A) Cyclic voltammograms of 2 mM AA and 0.4 mM EP at Fe(III)-PLH-CMWCN under the scan rate ranged from 10 to 100 mV s −1 , scan area: −500~800 mV.(B) The line curves of oxidation peak currents of AA and EP.

Figure 7 .
Figure 7. (A) Cyclic voltammograms of 2 mM AA and 0.4 mM EP at Fe(III)-PLH-CMWCNTs/AuE under the scan rate ranged from 10 to 100 mV s −1 , scan area: −500~800 mV.(B) The linear fitting curves of oxidation peak currents of AA and EP.

Figure 8 .
Figure 8. (A) Differential pulse voltammograms of AA and EP at the Fe(III)-PLH-CMWCNT in series of concentrations.Scan area: −200~400 mV.(B) The linear relationship between re current and AA concentration.(C) The linear relationship between response current a concentration.

Figure 8 .
Figure 8. (A) Differential pulse voltammograms of AA and EP at the Fe(III)-PLH-CMWCNTs/AuE in series of concentrations.Scan area: −200~400 mV.(B) The linear relationship between response current and AA concentration.(C) The linear relationship between response current and EP concentration.

Author
Contributions: B.H. performed the experiments and analyzed the data, he also proposed the fabrication methods and wrote the manuscript; G.L. and Z.H. performed the morphological analysis; C.Z. contributed reagents/materials/analysis tools.J.Y. proposed the fabrication methods; Y.C. and H.W. performed the experiments and editing.All authors have read and agreed to the published version of the manuscript.Funding: This work is supported by the Tianjin Science and Technology Commission (Grant No. 22JCQNJC00150).Institutional Review Board Statement: Not applicable.Informed Consent Statement: Not applicable.

Table 1 .
Comparison of analytical parameters between Fe(III)-PLH-CMWCNTs/AuE and the sensors previously reported by others.

Table 2 .
Determination of AA and EP in real-life samples by the prepared biosensor.