Xuefang Gu,
Xian Li,
Sijie Wu,
Jian Shi,
Guoqing Jiang*,
Guomin Jiang and
Shu Tian*
School of Chemistry and Chemical Engineering, Nantong University, Nantong 226007, P. R. China. E-mail: tian0429@ntu.edu.cn; jgq3518@163.com; Fax: +86-513-85012851; Tel: +86-513-85012856
First published on 28th December 2015
In this study, a novel mercapto-terminated trinuclear Ni(II) complex (Ni3) was synthesized and used as an electrocatalyst for the detection of hydrazine hydrate in real water samples. The as-prepared Ni3 molecule possesses six thiomethyl groups at its periphery and these SCH3 groups can react with Au electrodes to immobilize the Ni3 molecules on their surface through the formation of a self-assembled monolayer. The Ni3-modified Au electrode (Ni3/Au) demonstrates excellent electrocatalytic activity for the oxidation of hydrazine hydrate through a significant decrease in overpotential. The chronoamperometry study shows a diffusion coefficient (D) of 5.82 × 10−5 cm2 s−1 and a catalytic rate constant of 8.57 × 103 M−1 s−1. Using the square wave voltammetry (SWV) technique, this Ni3/Au electrode based hydrazine hydrate sensor exhibits a high sensitivity in quantitative analysis, and its detection limit could be as low as ∼0.07 μM with linearity ranging from 0.2 to 50 μM. In addition, due its good reproducibility, anti-interference performance, and long-term stability, the proposed sensor is capable of detecting trace levels of hydrazine hydrate in real water samples.
Due to the electroactive nature of hydrazine hydrate, electrochemical determination has proven to be a feasible and effective approach. Actually, as compared to the aforementioned methods, electrochemical techniques have several advantages such as easy to operate, rapid response, and high sensitivity. Previous literature have demonstrated that the electrooxidation of hydrazine is a four-electron irreversible process.13 However, the electron transfer rates of hydrazine oxidation at conventional electrodes (such as Au, Pt, or glass carbon electrodes) are relatively slow; therefore, direct electroanalysis is thus hindered by the accompanied large overpotentials. The common approach for lowering the over potential is through the introduction of electrocatalysts to fabricate chemically modified electrodes (CME). Various inorganic and organic materials with specific electrocatalytic properties have been reported, including metal nanoparticles,14–16 semiconductor nanoparticles,17,18 metallophthalocyanine complexes,13,19,20 hexacyanoferrate salt,21 and organic compounds with a hydroquinone structure.22,23 Sometimes, carbon nanotubes (CNTs) and graphene are used as the supporting substrate for electrocatalysts due to their high surface areas, excellent electric conductivity, and good chemical inertness.16,24–26 It should be noted that most of these modified electrodes are fabricated by physical strategies, e.g. dip-dry, drop-dry, mixing, and electrostatic adsorption. However, physically anchored films are likely to be eluted from the surface of CMEs during electrochemical measurements, and it is difficult to control the concentration of the deposited electrocatalyst, thus reducing the reproducibility of the modified electrode and repeatability of the result.
Self-assembled monolayer (SAM) techniques, in contrast, have distinct advantages over traditionally modified electrodes, including high stability, well-arranged modified layers, and convenient operation steps.13 More importantly, the ultrathin solid films of modifiers can significantly prompt direct electron transfer (DET) between the immobilized electroactive centers and the surface of electrodes. These advantages of SAM techniques have aroused increasing interests in CME construction, particularly in the modification of coinage-metal based electrodes. As is known, molecules containing mercapto groups can self-assemble on the surface of Au or Ag electrodes through the formation of Au–S or Ag–S covalent bonds. In this respect, if we could functionalize such electrocatalysts with SH or SCH3 groups, excellent catalytic ability and faster electron transfer between analytes and the electrode would be effectively integrated.
In our previous study, we reported the synthesis and usage of a mercapto-terminated hexanuclear Fe(III) complex,27,28 in which the Fe6 complex was chemically adsorbed on the surface of an Au electrode via self-assembly and a sensitive dopamine electrochemical sensor was constructed. Herein, we report the new mercapto-terminated Ni(II) complex, [Ni3(C3H6N4S)6(OH)6](Ni3), for the first time. The as-prepared Ni3 complex was immobilized on the surface of Au electrodes by self-assembly. Cyclic voltammetry, chronoamperometry, and electrochemical impedance spectroscopy methods were used to characterize and delineate the electrochemical behaviour of the Ni3 modified Au electrode (Ni3/Au). Moreover, the application of the Ni3/Au electrode in the electrocatalytic oxidation of hydrazine hydrate was investigated. Square wave voltammetry was used for the quantitative analysis of hydrazine hydrate in real water samples.
High resolution transmission electron microscopy (HRTEM) images of the Ni3/Au nanoparticles were taken on an FEI-Tecnai F20 (FEI, USA). To do this, colloidal gold was first synthesized according to the protocol of previous literature.29 Then, an aliquot of 200 μL Ni3 complex solution in ethanol (5 mg mL−1) was added to 2.0 mL as-prepared gold sol. The mixture was stirred for 10 h to form SAM of Ni3 molecules on the surface of the Au nanoparticles.
Chromatography detection of hydrazine derivation was performed on a Shimadzu LC-20A (Shimadzu, Japan) equipped with a diode array detector (DAD).
Cyclic voltammetry (CV), electrochemical impedance spectroscopy (EIS), and square wave voltammetry (SWV) were recorded on a CHI 660E electrochemical station (Shanghai ChenHua Instruments CO. LTD., China). A conventional three-electrode system was used. A bare or modified Au electrode was employed as the working electrode, a platinum plate as the auxiliary and Ag|AgCl (3 M KCl) as the reference electrode. All electrochemical measurements were conducted in an argon-purged (at least 15 min and maintained under an argon atmosphere during the entire experiment) solution at room temperature.
Prior to the modification, a bare gold disk electrode (2 mm diameter) was polished using aqueous slurries of alumina (1.0 down to 0.05 μm) and then washed ultrasonically in water/ethanol/water for 5 min to remove the physically adsorbed alumina. Furthermore, the electrode was electrochemically cleaned by cycling the electrode potential between 0.00 and +1.50 V in 0.5 M sulfuric acid (∼40 cycles, 50 mV s−1), until reproducible voltammograms were observed. The cleaned Au electrodes were then immersed into 2 mL of 5 mM Ni3 DMF solution for 24 h to ensure that saturated adsorption of the Ni3 molecules the surface of Au electrodes occurred through Au–S bonds. The electrodes were thoroughly rinsed with ethanol and water to remove physically adsorbed Ni3 molecules before electrochemical measurement.
The highlight of this study is the usage of the electrocatalytic property of the Ni3 complex to lower the overpotential and enhance the sensitivity in hydrazine hydrate detection, thus it is first necessary to verify that the modified electrode was successfully built. In this study, although we cannot visually observe the surface of the Ni3 modified electrode using a simple method, we managed to immobilize the Ni3 complex on Au nanoparticles and obtained HRTEM images of the Ni3/Au nanoparticles (Fig. 1b). Because Ni3 molecules can self-assemble on the surface of Au nanoparticles, they certainly can be modified on the surface of Au electrodes by the same chemical reaction. As shown in Fig. 1b, several core–shell structures consisting of dark centers and light-colored edges are observed, which can be more clearly observed in the inset of Fig. 1b. The dark centers are Au nanoparticles with an average diameter of ∼12 nm. All the nanoparticles were wrapped by complex shells with a thickness of ∼1 nm (in good agreement with the size of Ni3 measured using the SHELXS-97 program), which thus could be assigned to Ni3 molecules. These images may be used as indirect evidence for the successful immobilization of the Ni3 complex on the surface of the Au electrodes.
Fig. 1c compares the CVs of theNi3/Au and bare Au electrodes in 0.1 M PBS (pH 7.0). As can be observed, the bare Au electrode did not show any noticeable redox process because there was no redox species in the electrolyte. In contrast, after modification of the Ni3 complex, a couple of well-defined redox peaks were clearly observed, which could be attributed to the Ni(III)/Ni(II) redox couple. The formal potential (E1/2) was ∼0.261 V, and the cathodic and anodic peaks were at +0.215 V and +0.307 V with ΔEp = Epa − Epc = 92 mV, which is slightly greater than the theoretical 59 mV for fast one-electron transport. In addition, the ratio of the anodic peak current to the cathodic current Ipa/Ipc is approximately 0.94, which indicates a quasi-reversible electrochemical reaction for the immobilized Ni complex. The direct electrochemical signal of the Ni3 complex further demonstrated the successful modification of the Au electrodes. In this study, Ni3 was immobilized on the surface of Au electrodes via self-assembly. The formation of this monolayer could establish a direct electron transfer between the electroactive center of Ni3 and the Au electrodes, which benefits the fabrication of an electrochemical sensor with high sensitivity and rapid response. Moreover, the CV responses of these two different electrodes in 5 mM Fe(CN)63− (Fig. 1d) may also be evidence for the successful construction of the Ni3/Au electrode. Compared with the Ni3/Au electrode, the redox probe showed more reversible behavior at the bare Au electrode, thus indicating that the Ni3 monolayer blocked electron transfer between the probe and the surface of the Au electrode.
EIS of the Ni3/Au and bare Au electrodes were also measured to investigate the interface properties of the modified electrode; the Nyquist plots for both electrodes are shown in Fig. 2b. As observed, after modification of the Ni3 complex on bare Au electrodes, the plot exhibited a much larger semicircle in the high frequency region. These results indicate that the modification of Ni3 can increase the electron transfer resistance (Ret), thus confirming the successful immobilization of Ni3 on the surface of the Au electrodes. By fitting the data with the Randles equivalent circuit, the values of electron transfer resistance, Ret, at the bare Au electrode and Ni3/Au electrode, R′et, were estimated to be 74 and 428 Ω, respectively. Using these data, we calculated the surface coverage of the Ni3 molecules on the Au electrodes (θ′) according to θ′ = 1 − Ret/R′et = 1 − 78/428 = 0.82, which was in good agreement with the calculated result using the gold oxide reduction current.
The concentration of the electroactive substance was evaluated according to the Laviron eqn (1) and (2) as follows:30
![]() | (1) |
![]() | (2) |
The decrease in overpotential and increase in anodic peak current indicate a typical EC process, wherein the voltammetric response of hydrazine is catalytically mediated by the redox processes of the Ni3 complex. Previous literatures have proven that Ni(III) can catalyze the oxidation of hydrazine, which starts with the formation of a Ni(III)–hydrazine complex, using the lone pair electrons on the N atoms and the unoccupied orbit on the central atom Ni(III).31,32 In this study, we propose the following general mechanism for the oxidation of hydrazine at the Ni3/Au electrode:
Ni(II) complex − e → Ni(III) complex | (3) |
Ni(III) complex + N2H4 → [Ni(III)N2H4 complex]adduct | (4) |
[Ni(III)N2H4 complex]adduct → [Ni(II)N2H3˙]adduct + H+ | (5) |
[Ni(II)N2H3˙]adduct → Ni(II) complex + N2H3˙ | (6) |
N2H3˙ + 3H2O → N2 + 3H3O+ + 3e | (7) |
Overall reaction: N2H4 + 4H2O → N2 + 4H3O+ + 4e | (8) |
Eqn (3) depicts the redox process of the nickel species confined in the Ni3 molecules. The interaction of the Ni(III) center atom with N2H4 results in the formation of an adduct (eqn (4)). The adduct undergoes an internal reaction leading to the formation of the intermediate Ni–N2H3˙ complex (eqn (5)), which is also the rate-determining step. Eqn (6) and (7) represent the regeneration of the original Ni(II) complex and the subsequent chemical process, respectively. Eqn (8) is the chemical equation of the overall reaction, which can occur on a bare Au electrode surface.
To further characterize the electrode/solution interface behavior towards hydrazine hydrate oxidation, CVs of the Ni3/Au electrode in 0.1 M Na2SO4 containing 50 μM hydrazine hydrate at various scan rates were recorded and the results are shown in Fig. 4a. As can be observed, the oxidation peak currents increase as the scan rate increases. Fig. 4b shows the linear dependence of the peak currents on scan rate from 25 to 800 mV s−1. The linear regression equations is y = 5.681x + 0.924 (R = 0.9975), which indicates that the electrocatalytic oxidation of hydrazine hydrate is a surface-confined process. This result is in good agreement with the aforementioned rate-determining step rate (eqn (5)).
The CVs at different scan rates further evidence the proposed EC mechanism. As shown in Fig. 4a, new cathode current peaks appear in the reverse scans. The potential difference between the cathode current peak and the oxidation peak of hydrazine hydrate is only about 40 mV, which is obviously less than that of the charge transfer process (59 mV/n). In an actual experimental operation, these cathode current peaks might not be readily observed at a relatively slow scan rate, due to no obvious intermolecular force acting on the adsorption layer. However, these peaks become increasingly clear with an increase in the scanning rate. The new peaks could be attributed to the desorption behavior of the [Ni(II)N2H3˙]adduct from the electrode surface (eqn (6)).
Moreover, only a slight increase in the oxidation peak potentials is observed, which suggests a fast electron transfer rate. This could be ascribed to the Ni3 SAM that immobilized on the surface of the Au electrodes, through which the considerable electrocatalytic activity of the Ni3 complex and the DET between hydrazine and the electrode were achieved (see below for the calculated value of the electrocatalytic rate constant, kcat). The fast response can also be verified via the chronoamperometry (CA) method (Fig. 5), wherein the oxidation currents stabilize rapidly within about 10 s. In addition, the facilitation for the diffusion of hydrazine molecules to the catalytic sites might be another factor for the fast response (see below for the detailed calculation of the diffusion coefficient, D).
The advantageous electrocatalytic reactivity of the modified electrode in the oxidation of hydrazine was tested using the CA method, which may offer informative and quantitative thermodynamic data employing the Cottrell effective constant. To determine the diffusion coefficient (D) and catalytic rate constant (kcat) for the oxidation of hydrazine on the Ni3 modified electrode, CA was carried out at different concentrations (10–40 μM) of hydrazine under a potential of 0.4 V and the results are shown in Fig. 5. The Cottrell equation eqn (9) was used to calculate the diffusion coefficient for hydrazine in this study given as follows:28
![]() | (9) |
The catalytic rate constant (kcat, M−1 s−1) for the electrochemical reaction between hydrazine and the redox sites of Ni3 molecules can also be evaluated by chronoamperometry through eqn (10) as follows:17,21
![]() | (10) |
Electrode | Fabrication method | Detection method | Linear range (μM) | LOD (μM) | Sensitivity (nA μM−1) | Ref. |
---|---|---|---|---|---|---|
PdNPs/MWCNT modified GCE | Coating/electro-deposition | LSV | 56–157 | 10 | — | 34 |
Curcumin/MWCNT modified GCE | Drop-dry | Chronoamperometry (I–t) | 2.0–44 | 1.4 | 22.9 | 22 |
Cu–Pd/SPE | Electrodeposition | Flow injection amperometry | 2–100 | 0.27 | 210 | 35 |
Au@Pd core–shell/rGO–GCE | Drop-dry | RDE (500 rpm) | 2–40 | 0.08 | 270.2 | 14 |
GNPs/Ch/GCE | Eletrodeposition | LSV | 0.5–500 | 0.1 | 84.3 | 33 |
ZrHCFc/Au–PtNPs/nanofibers modified GCE | Coating | Amperometry at RDE | 0.15–112 | 0.09 | ∼52 | 21 |
PEG-CdS NPs modified Au | Coating-dry | Chronoamperometry (I–t) | 0.1–1 | 0.06 | 890 | 18 |
ZnO/CNTs/HPDB/CPE | Mixing | SWV | 0.02–0.7 | 0.009 | 184.8 | 17 |
FePc-linked-mPy-modified Au | LBL self-assembly | SWV | 13–92 | 5 | 16.2 | 13 |
EPPGE–SWCNT–Ni | Coating/electro-decoration | LSV | — | 5.3 | 517 | 26 |
NiHCF@TiO2 NPs modified GCE | Coating-dry | DPV | 0.2–1 | 0.11 | 158.2 | 36 |
MWCNT/Ni nanocomposites GCE | Drop-dry | Amperometry | — | 0.3 | 104.6 | 31 |
This work, Ni3 modified Au | Self-assembly | SWV | 0.2–50 | 0.07 | 136.2 | — |
However, when the concentration of hydrazine was larger than 50 μM, the response of SWV gradually deviated from the calibration curve. Furthermore, when the concentration exceeded 0.2 mM, the SWV curves showed apparent differences with those of smaller concentrations (Fig. S3, ESI†). The oxidation peek potential positively shifted and new peaks corresponding to the oxidation of hydrazine at the bare Au electrodes appeared. This observation could be attributed to the saturation of the active sites in the Ni3 complex molecules, which implies that the proposed sensor is particularly suitable for the detection of hydrazine in real samples with extremely low concentrations.
To verify the reproducibility and stability of this electrode, the SWV curves of a 50 μM hydrazine solution were recorded for twenty consecutive detections (Fig. S4, ESI†). The result showed a relative standard deviation (RSD) of 4.7%. As for six parallel fabricated electrodes, the RSD was 8.6%. The modified electrode was then stored in Ar at 4 °C over 15 days and 94% of its original current value was maintained. These results indicate the excellent stability and reliability of the sensor towards hydrazine determination. The good reproducibility of this electrode might be associated with a combination of following factors: (i) the self-assembly method allows the Ni3 complex to functionalize the electrode surface via Au–S covalent bonds, and the amount of the electroactive substance on the electrode surface is relatively constant under a saturated adsorption, thus achieving a more stable signal than the physically fixed methods reported in some other literature; (ii) the closely arranged Ni3 molecules occupy most of the Au surface, thus making it difficult for the adsorption of unwanted interferences; and (iii) the electrocatalytic reaction occurs at the center of the Ni3 molecules, thus even if there was any adsorption on the electrode surface, the influence on the measured signal should be negligible.
The influence of various coexisting ions on the determination of hydrazine was investigated by adding various foreign species into 5 μM hydrazine solution. An approximately 100% ± 7.3% recovery caused by the addition of foreign substances is acceptable in trace analysis. The results reveal that K+, Na+, Ca2+, Mg2+, Fe2+, Cu2+, Zn2+, NO2−, NO3−, Cl−, Br−, SO42−, CO32−, and PO43− (>200 fold) and sucrose, glucose, fructose, tartaric acid, and citric acid (>100 fold) have no obvious interference with hydrazine detection. However, the addition of 20-fold quantities of ascorbic acid and an equivalent concentration of NH2OH led to a noticeable variation of peak current. This is reasonable because the oxidation potentials of ascorbic acid and NH2OH are close to that of hydrazine.
Samples | Original (μM) | Added (μM) | Found at Ni3/Au (μM) | Found in HPLC (mM) | RSD (%) | Recovery (%) |
---|---|---|---|---|---|---|
Drinking water | 0 | 2 | 1.97 | 1.95 | 4.2 | 98.5 |
0 | 5 | 4.86 | 4.92 | 2.2 | 97.2 | |
0 | 10 | 10.25 | 10.10 | 3.6 | 102.5 | |
Tap water | 0 | 2 | 2.12 | 1.93 | 4.1 | 106.0 |
0 | 5 | 4.83 | 5.06 | 4.9 | 96.6 | |
0 | 10 | 9.91 | 9.95 | 3.5 | 99.1 | |
River water | 0 | 2 | 1.95 | 1.88 | 6.7 | 97.5 |
0 | 5 | 5.34 | 5.21 | 5.3 | 106.8 | |
0 | 10 | 9.87 | 10.07 | 3.8 | 98.7 |
Footnote |
† Electronic supplementary information (ESI) available: The crystallographic data of the Ni3 complex, Fig. S1 and S2. CCDC 1435763. For ESI and crystallographic data in CIF or other electronic format see DOI: 10.1039/c5ra23809a |
This journal is © The Royal Society of Chemistry 2016 |