Insights into the Electrochemical Behavior of Mercury on Graphene/SiC Electrodes

Abstract

Fast and real time detection of Mercury (Hg) in aqueous solutions is a great challenge due to its bio-accumulative character and the detrimental effect on human health of this toxic element. Therefore, development of reliable sensing platforms is highly desirable. Current research is aiming at deep understanding of the electrochemical response of epitaxial graphene to Mercury exposure. By performing cyclic voltammetry and chronoamperometry measurements as well as density functional theory calculations, we elucidate the nature of Hg-involved oxidation-reduction reactions at the graphene electrode and shed light on the early stages of Hg electrodeposition. The obtained critical information of Hg behavior will be helpful for the design and processing of novel graphene-based sensors.

1. Introduction

Extensive anthropogenic activities (agriculture, heavy industry) are causing increased pollution of potable water sources, soil, and air with toxic substances, such as volatile organic compounds (VOCs) [1,2], pesticides [3,4], and heavy metals [5,6]. The most prominent consequence of mentioned pollution is contamination of food products such as fish [7], vegetables [8], and meat [9] via introduction of the listed pollutants in the ground and sea water, causing enhanced mortality and other health effects in poisoned humans. Among others, mercury (Hg) is regarded as one of the most toxic chemical elements [10] since long-term exposure to its complexes may result in memory problems [11], muscle weakness [12], kidney diseases [13], acrodynia [14], brain dysfunction [15], and inhibition of the human thioredoxin system [16]. Regarding Hg poisoning, it is imperative to develop viable preventive strategies towards its fast and real-time recognition in water followed by its complete removal. In this context, international community and governmental agencies in different countries have developed strict requirements concerning the acceptable limit of Hg²⁺ in drinking water, varying from 5.0 to 30.0 nM [17,18]. Therefore, it is natural that detection systems for reliable mercury sensing have been extensively developed during last decades [19,20]. Apart from the traditional analytical methods for Hg²⁺ detection (atomic absorption/fluorescence spectroscopy, inductively coupled plasma mass spectrometry, liquid chromatography-mass spectrometry [21]) and highly sensitive amperometric methods exploiting field-effect transistor (FET)-type discriminative sensors [22,23,24,25] that usually require complicated sample/device preparation procedures, electrochemical methods are more convenient ways to facilitate real-time monitoring of mercury at nanoconcentrations below permissible levels and have therefore attracted widespread attention due to their portability and simplicity [26,27]. In this regard, great efforts have been made to find an appropriate working electrode material—the main component of the typical electrochemical system—which is mainly responsible for the sensing performance. To be more exact, to attain a high sensitivity, the surface of such an electrode should provide a large enough number of electrochemically active sites available to accommodate and bind as many Hg species as possible.

Graphene and its derivatives, namely graphene quantum dots (GQDs), graphene oxide (GO), and reduced graphene oxide (rGO), have been demonstrated as unique low-dimensional materials which are capable of sensing individual adsorbates, enabling detection of even single-electron charge transfer events [28]. Such properties create excellent prerequisites of exploring these materials as high performance sensors [29]. At the same time, the use of graphene-family materials for electrochemical detection of mercury primarily limits one to modification and/or functionalization of the glassy carbon electrode (GCE) to enhance the adsorption energy of Hg species and consequently the intensity of the analytical signal [30,31,32,33,34,35,36,37,38,39,40,41,42]. Although the modified GCE demonstrates good short-term reversibility and repeatability towards Hg detection, its exploitation implies additional preparation steps. Furthermore, the adhesion strength of graphene flakes placed on its surface is not clear and requires using a binder (for example, Nafion) due to a lack of dangling bonds on the GCE. Poor adhesion can be problematic for long-term stability of the working electrode. Another strategy is to exploit 4H-SiC covered with graphene (also called epitaxial graphene, Gr/SiC) as the working electrode [43]. This kind of graphene is chemically stable due to the interaction with substrate [44], but it still demonstrates the key benefits of exfoliated graphene as a sensing platform [45]. Particularly, epitaxial graphene offers a combination of advantages over other graphene-family materials (especially, CVD graphene that has, in most cases, mosaic structure with rotated domains [46,47]): large surface area, high quality of monolayer graphene, thickness uniformity, wide potential window, high signal-to-noise ratio, transfer-free technology, and direct sublimation growth without precursors [44,48,49]. Despite the fact that the basal plane of epitaxial graphene has a lower number of electroactive sites compared to graphite (high number of edge sites) and CVD graphene (highly reactive domain boundaries), the signal readout of the sensor is higher for this two-dimensional material due to its higher conductivity and lower noise in comparison to CVD graphene and multilayer graphene. In this context, a balance between graphene quality and density of the electroactive sites must be reached. All these advantages provide excellent prerequisites for development of the monolithic wafer-scale sensorics. Taking the aforementioned into account, how the Gr/SiC system responds to Hg exposure is of interest. Recently, we have been studying the electrochemical activity of Gr/SiC towards the Pb²⁺/Pb⁰ redox couple and revealed a possibility to detect critically low Pb concentrations in aqueous solutions [50,51]. Nevertheless, the behavior of Hg on epitaxial graphene has not been reported so far and, thus, any attempts to elucidate the nature of this behavior are highly demanded. Here, by performing cyclic voltammetry and chronoamperometry measurements, we extend our previous electrochemical studies to mercury with the aim to investigate the electrochemical activity of Gr/SiC towards the Hg²⁺/Hg⁰ redox reaction and to uncover the nature of the Hg kinetics during early stages of Hg electrodeposition. We believe that knowledge on Hg kinetics will be beneficial to develop an electrochemical sensing platform based on epitaxial graphene for Hg detection.

2. Materials and Methods

Epitaxial graphene on on-axis 4H-SiC (Gr/SiC) was grown through high temperature thermal decomposition of Si-face (0001)4H-SiC substrate (7 × 7 mm²) in argon atmosphere by means of an inductively heated graphite container with a well-controlled temperature profile [52]. Optical reflectance mapping [53] showed that most of the substrate surface is covered with monolayer (1 ML) graphene, whereas bilayer (2ML) graphene inclusions are rarely observed. All room-temperature electrochemical measurements were performed by using a computer-controlled potentiostat (Autolab, EcoChemie, Metrohm, Utrecht, The Netherlands). The o-ring-type three-electrode electrochemical cell consists of Gr/SiC as a working electrode, Ag/AgCl as a reference electrode, and platinum wire as a counter electrode. More details on the design of the electrochemical cell have been reported previously [54]. To gain deep insights into the redox behavior of mercury, we performed cyclic voltammetry measurements within a potential region from −0.8 V to +0.5 V in two different buffer solutions (0.01 mol·L⁻¹ and 0.1 mol·L⁻¹ HClO₄ in Milli-Q-water) with 0.1 mM Hg²⁺ (purity of Hg(NO₃)₂ is higher than 99%). We have chosen HClO₄ buffer as a model electrolyte solution to monitor the Hg redox reactions at the epitaxial graphene electrode surface. Our choice can be explained by the fact that, compared to other chemicals, the perchlorate ions (ClO₄⁻) exhibit a noncomplexing characteristic with respect to metal cations in aqueous solutions [55,56,57]. This means that electrochemical measurements performed in the frames of the current work will exclusively provide information on Hg-involved oxidation–reduction reactions, but not on the reactions involving more complicated chemical complexes. In order to study the Hg redox behavior and kinetics at the epitaxial graphene electrode, we used the Hg concentration of 0.1 mM, which is high enough to provide an intense electrochemical signal. The scan rate was 20 mV/s. The electrochemical reactions are expected to occur at the area of 3.1 mm². To shed light on the nature of the kinetics of Hg, we recorded the current–time transients during the early stages of Hg electrodeposition on Gr/SiC. The Scharifker–Hills methodology was applied to define the nucleation mechanism [58]. The interaction between Hg and graphene was investigated based on density functional theory (DFT) calculations performed by using Gaussian 16 Rev. B.01 package [59]. Circumcoronene (C₅₄H₁₈) has been chosen as a model of graphene. All calculations were carried out using PBE1PBE level of theory with empirical dispersion correction [60,61]. The 6–31G basis set was used for carbon, oxygen, and hydrogen atoms, while the basis set developed by the Stuttgart–Dresden–Bonn group (SDD) was utilized for the Hg [62]. Noncovalent interaction (NCI) analysis has been performed using the Multiwfn program to better understand the Hg–carbon bonding characteristics [63].

3. Results and Discussion

Figure 1 exhibits the voltammetric response of an epitaxial graphene electrode in solutions containing the supporting electrolyte (0.01 M HClO₄) and mercury salt. An important point that can be noticed is the presence of a double layer region (between +0.5 V and −0.4 V) without any faradaic processes at the electrode immersed in pure electrolyte. A rapid increase of cathodic current occurred only below −0.6 V due to the hydrogen evolution reaction (HER) on Gr/SiC; see the deep orange colored curve in Figure 1. The 0.1 mM Hg²⁺ solution shows a reduction peak R₁ ranging from 0 V to +0.18 V, followed by the corresponding oxidation wave in the potential range from +0.19 V to +0.42 V, which can be attributed to Hg redox reactions, see dark blue colored curve in Figure 1. The voltammogram also shows additional features (R₂ plateau in the range −0.29 V to −0.41 V and R₃ peak located at −0.52 V) possibly associated with overpotential deposition (opd) of Hg and oxygen electrosorption reactions [64]. The intense split oxidation peak with two distinguishable components (O₁ and O₂) related to Hg stripping is indicative of a two-step oxidation reaction at the electrode surface; see the inset in Figure 1 [65]. The total charge density corresponding to Hg stripping and plating can be estimated by the background-corrected integration of the area under the oxidation and reduction peaks (see Figure 2a) using the following formula:

$$Q_{C,A}=\frac{1}{v}{{\displaystyle \int }}_{V_i}^{V_f}I\left(V\right)dV$$

(1)

where $Q_{C,A}$ is cathodic and anodic surface charge density, $v$ is the scan rate, $I$ is the current density, $V_i$ and $V_f$ are the initial and final voltages, respectively. The integrated cathodic charge density of the C-V is 17 mC∙cm⁻², which is significantly lower than the value of 153 mC∙cm⁻² obtained for the anodic peak. The Q_C/Q_A ratio is estimated to be 8.9, which suggests electrochemically quasireversible redox reaction.

A closer look at the asymmetry of the oxidation and reduction peaks (see Figure 2b,c) enables assigning the components O₁ at 0.236 V and O₂ at 0.258 V for the oxidation process to two well-defined steps (Hg⁰ − 1e⁻ = Hg¹⁺ − 1e⁻ = Hg²⁺), as well as R₁^′ at 0.09 V and R₂^′ at 0.128 V components for the reduction process to two one-electron steps (Hg²⁺ + 1e⁻ = Hg¹⁺ + 1e⁻ = Hg⁰), respectively. Similar voltammetry response has also been observed for Hg at the partially oxidized graphene/poly(3,4-ethylenedioxythiophene):poly(styrenesulfonate) nanocomposite film-modified electrode [66], Hg at the Pt electrode [64], and Hg at the activated carbon modified glassy carbon electrode [67].

According to literature data, the redox behavior of Hg is strongly dependent on the scan rate [66] and pH level [67]. Particularly, it was shown that at high scan rates (>20 mV/s), mercury oxidation reaction takes places in two steps, which was evidenced by the presence of two oxidation peaks, while at low scan rates (<20 mV/s), the mercury stripping occurs only in one step [66]. Furthermore, Radhi et al. observed one oxidation peak in acidic electrolytes, and two oxidation peaks in alkaline solutions (at pH 8.5 to 10.5) [67]. The latter can be explained by the occurrence of two competitive oxidation processes: Hg⁺ − e⁻ = Hg²⁺ and Hg⁰ − 2e⁻ = Hg²⁺, respectively. Bearing this in mind, we then performed additional cycling voltammetry measurements by exploiting a higher concentration of perchloric acid in the electrolyte solution (0.1 M HClO₄), but using the same Hg²⁺ concentration as in the initial experiment. A cyclic voltammogram recorded for 0.1 mM Hg²⁺ in 0.1 M HClO₄ with a scan rate of 20 mV∙s⁻¹ is shown in Figure 3a. Two distinguishable peaks associated with the redox couple of Hg²⁺/Hg⁰: cathodic peak at 0.043 V and intense anodic peak at 0.244 V, can be clearly seen, demonstrating that mercury undergoes a two-electron transfer redox reaction in more concentrated buffer solution. In this case, only one oxidation peak instead of two was observed after several cycles. The contribution of the shoulder peak is negligibly small. The reduction peak in the higher concentration of HClO₄ is still quite asymmetric, possibly indicating two-step electron transfer process. Therefore, the mechanism that underlies the reduction and oxidation reaction at the epitaxial graphene surface can be expressed by the following equations:

$$\{\begin{array}{c}{\mathrm{Hg}}^{2+}+1e^{-}\to {\mathrm{Hg}}^{1+}+1e^{-}\to {\mathrm{Hg}}^0 \left(reduction: cathodic process\right)\\ {\mathrm{Hg}}^0-2e^{-}\to {\mathrm{Hg}}^{2+} \left(oxidation: anodic process\right)\end{array}$$

(2)

The comparison of the one-step and two-step Hg-involved redox reactions at the epitaxial graphene electrode surface is visualized in Figure 3b. It is important to note that the peak-to-peak separation, ∆E_p, and the peak current ratio, I_pa/I_pc, are about 201 mV and 7.3, respectively. This suggests that the Hg redox process at the epitaxial graphene working electrode is an electrochemically quasireversible process [68,69]. To shed more light on the nature of the oxidation and reduction reactions, we also estimated the electron transfer rate constant for the plating and stripping process. At ∆E_p > 200 mV, the electron transfer rate constant can be calculated by means of the Klingler and Kochi relationship [70]:

$$k^0=2.18\left[D\alpha n\nu F/{\left(RT\right)}^{1/2}\right]\exp \left[-\left({\alpha }^{2}nF/RT\right)\mathsf{\Delta }{E}_P\right]$$

(3)

where F is the Faraday constant, R is the gas constant, T is a temperature, α is the transfer coefficient (typically a value of 0.5 is assumed), D is the diffusion coefficient of oxidative (reduced) species in cm²∙s⁻¹, n is the number of electrons transferred, v is the scan rate in V∙s⁻¹. The unknown diffusion coefficients of the electroactive species for both oxidation and reduction process for quasireversible system at 298 K can be estimated by using Randles–Ševcik equations [68,69]:

$$I_{p,c}^{quasi}=-\left(2.65\times {10}^5\right)n^{3/2}AC{D}_c^{1/2}{\nu }^{1/2}$$

(4)

$$I_{p,a}^{quasi}=+\left(2.65\times {10}^5\right)n^{3/2}AC{D}_a^{1/2}{\nu }^{1/2}$$

(5)

where, $I_{p,c}^{quasi}$ and $I_{p,a}^{quasi}$ are the cathodic and anodic peak current densities in A∙cm⁻², D_a and D_c are the diffusion coefficients of the oxidative and reduced Hg species, C is the bulk concentration of oxidative species in solution, and A is the area of the working electrode. The estimated parameters are listed in

Table 1. Parameters describing the electrochemical behavior of the Hg²⁺/Hg⁰ redox couple at room temperature at the epitaxial graphene electrode.

Parameter	Anodic Process Hg0 − 2e−→Hg2+	Cathodic Process Hg2+ + 2e−→Hg0
Current density, mA/cm2	35.75	−4.88
Potential, V	0.244	0.043
Surface charge density, mC/cm2	90	16
Electron transfer rate constant, 10−2 × cm∙s−1	6.4	0.89

.

It is obvious that the rate of the electron transfer for the anodic process is predicted to be higher than the rate of electron transfer for the cathodic process. As a result, the oxidative current peak is expected to increase more rapidly with increasing mercury concentration than the reduction current peak and can, therefore, be used as an analytic signal for mercury sensing in aqueous solutions. The knowledge on Hg redox reactions and kinetics on pristine epitaxial graphene can be considered as a starting point for further investigation and development of an epitaxial graphene-based sensing platform for real-time detection of mercury. Regarding selectivity, information on the correct positions of the Hg-related reduction and oxidation peaks is of great technological importance, since it can be helpful to design the sensors, which will be cross-sensitive to specific heavy metals. This is due to the fact that each metal has unique redox potential. Therefore, electrochemical measurements (square wave anodic stripping voltammetry, for instance) will enable one to distinguish between different metals. To be more specific, in the case of the epitaxial graphene working electrode, the corresponding oxidation peaks for the three most toxic heavy metals, namely Cd, Hg, and Pb, are located at −0.79 V, 0.24 V, and −0.43 V [50,71], which creates excellent prerequisites for discriminative analysis without overlapping redox peaks.

To better understand how the epitaxial graphene influences the Hg nucleation-growth process, we next carried out chronoamperometry measurements and recorded current–time transients during Hg electrodeposition. Typical current density–time transients at different deposition potentials are demonstrated in Figure 4a. In their early work, Scharifker and Hills originally proposed [58] two probable models of metal deposition on arbitrary substrates, namely instantaneous nucleation and progressive nucleation. In the case of the first nucleation mechanism, all the Hg nuclei are formed simultaneously, while the second mechanism implies that new Hg nuclei are gradually created during potential stepping. From a theoretical point of view, the current–time transients corresponding to instantaneous nucleation and progressive nucleation can be described by the following simplified relationships.

$$\{\begin{array}{c}{\left(\raisebox{1ex}{$I_{inst}$}\!\left/ \!\raisebox{-1ex}{$I_{max}$}\right.\right)}^2=1.9542{\left(\raisebox{1ex}{$t$}\!\left/ \!\raisebox{-1ex}{$t_{max}$}\right.\right)}^{-1}{\left\{1-\exp \left[-1.2564\left(\raisebox{1ex}{$t$}\!\left/ \!\raisebox{-1ex}{$t_{max}$}\right.\right)\right]\right\}}^2\\ {\left(\raisebox{1ex}{$I_{prog}$}\!\left/ \!\raisebox{-1ex}{$I_{max}$}\right.\right)}^2=1.2254{\left(\raisebox{1ex}{$t$}\!\left/ \!\raisebox{-1ex}{$t_{max}$}\right.\right)}^{-1}{\left\{1-\exp \left[-2.3367{\left(\raisebox{1ex}{$t$}\!\left/ \!\raisebox{-1ex}{$t_{max}$}\right.\right)}^2\right]\right\}}^2\end{array}$$

(6)

A comparison of the theoretical current–time curves with experimental ones presented in Figure 4b indicates that the initial kinetics of Hg species onto the epitaxial graphene electrode is governed by the three-dimensional instantaneous growth-nucleation mechanism, which is in agreement with the Hg electrodeposition mechanism reported for boron-doped diamond electrodes [72] and vitreous carbon electrodes [73]. At the initial stages, the ${\left(I/I_{max}\right)}^2$ parameter increases (which is associated with enlarging surface density of Hg nuclei) and then decreases gradually after it reaches some maximum dependent on the applied potential. During the early stages of Hg nucleation, the time corresponding to the maximum value of the ${\left(I/I_{max}\right)}^2$ parameter shortens with the increase in the deposition potential.

Further analysis of the experimental current–time transients (Figure 5) makes it possible to determine the diffusion coefficient of the mercury species, which can be calculated by using the Cottrell equation [74]:

$$I=D^{1/2}nFAC{\pi }^{-1/2}{t}^{-1/2}$$

(7)

From the slope of a linear plot of I vs. t^−0.5 at different deposition potentials (Figure 5), the average value of the diffusion coefficient is found to be approximately 6.63 × 10⁻² cm²·s⁻¹, which is significantly higher than the diffusion coefficient of Hg on a vitreous carbon electrode (1.4 × 10⁻⁵ cm²·s⁻¹) [73] and on a boron-doped diamond electrode (~10⁻⁵ cm²·s⁻¹) [72]. As has been shown in our previous work, Hg species can freely diffuse across the graphene surface with a negligible energy barrier [75]. Therefore, such a high diffusion coefficient implies barrierless surface migration of Hg at the epitaxial graphene electrode, suggesting a limited number of electroactive sites at the graphene surface. The average number density of nucleation sites (N₀) on the Gr/SiC surface was determined by using the following formula [58]:

$$N_0=0.065{\left(\frac{1}{8\pi C{V}_m}\right)}^{1/2}{\left(\frac{nFC}{I_{max}{t}_{max}}\right)}^2$$

(8)

where n is the number of electrons involved, F is the Faraday constant, C is the concentration of species in the bulk, V_m is the molar volume, t_max is the peak time, and I_max is the peak current density. N₀ was estimated to be as low as 5.59 × 10³ cm⁻².

A high diffusion coefficient of Hg and low number of active nucleation sites originating from weak interaction between Hg and pristine epitaxial graphene do not promote fast charge transfer reactions at the electrode surface and thus the sensitivity of the nominally pristine epitaxial graphene with respect to Hg is expected to be poor. Therefore, this material needs to be modified, possibly through introduction of additional electroactive sites (carbon vacancies, for instance) to attain desirable sensing performance, while maintaining the graphene’s quality. As has been shown in our previous work [76], the carbon vacancies can significantly improve the adsorption energy of Hg on graphene.

To gain better understanding of the nature of the Hg electroreduction (Hg²⁺→Hg⁰) at the graphene surface, we carried out DFT calculations by mimicking realistic reduction conditions with consideration of the hydration shell for the Hg²⁺ cation. Figure 6a demonstrates the first hydration shell structure around the Hg²⁺ ion. Such a structure is characterized by six water molecules with regular octahedral geometry.

The mean bond length between the oxygen atom of the water molecule and Hg²⁺ ion is 2.34 Å. The Hirshfeld charge located on the Hg ion is predicted to be +0.643. Interestingly, after addition of two electrons to the [Hg(H₂O)₆]²⁺ complex, the Hg atom becomes neutral with a negligibly small Hirshfeld charge of +0.0036 due to breaking of the Hg–O bonds (Figure 6b). This implies a complete reduction of the mercury ion. In this case, the distance between Hg⁰ and oxygen is about 3.22 Å for the three closest O atoms and 3.55 Å for the others. At the next stage, we studied the behavior of the optimized [Hg(H₂O)₆]²⁺ complex at the graphene electrode surface. As can be seen in Figure 7a, the octahedral geometry of the first hydration shell is completely broken, and Hg ions form only three chemical bonds with water molecules (trigonal geometry). In this case, the Hirshfeld charge on the Hg ion is approximately +0.571, probably due to additional charge transfer from graphene to metal.

To simulate the reduction process at the graphene surface, we then added two electrons to graphene and allowed the [Hg(H₂O)₆]²⁺/(graphene+2e⁻) structure to be relaxed. The result of structural optimization is presented in Figure 7b. The Hg atom having the positive charge of +0.044 prefers to sit at the hollow site of graphene, with adsorption height of 3.15 Å. This finding indicates that the added electrons are completely employed to reduce the charge of the Hg ion.

Noncovalent interaction (NCI) analysis allowed us to elucidate the nature of [Hg(H₂O)₆]⁰ –graphene interaction. For graphene interacting with the [Hg(H₂O)₆]⁰ complex, we observed the well pronounced green-colored area located at the hollow site seen in Figure 8a, which can be interpreted as a nonbonding interaction region.

This clearly indicates that van der Waals interaction between Hg and graphene dominates. The analysis of electron density and electron localization function (ELF) gives more information on charge redistribution in the [Hg(H₂O)₆]⁰–graphene system, see Figure 8a,b. It can be seen that there is no electron localization overlap between Hg and graphene, also confirming a pure physisoprtion of Hg on graphene. By performing DFT calculations, we revealed that the interaction of reduced Hg species with graphene surface occurs mainly through weak van der Waals interaction. This finding explains the experimentally derived high diffusion coefficient of Hg and low number of active nucleation sites. Due to the weak interaction, Hg species can freely migrate across the graphene surface without energy barriers. We also modeled the realistic reduction process considering the divalent Hg ion with its first hydration shell and found that added electrons are completely employed to reduce the charge of the Hg ion. This shows the principal possibility of Hg electroreduction at the graphene surface.

4. Conclusions

The results obtained in this study show that the electrochemical redox behavior of Hg²⁺ at the epitaxial graphene working electrode is quite complicated and strongly dependent on the concentration of perchloric acid in the electrolyte solution. In 0.01 M HClO₄ buffer solution, the redox process occurs in two well-defined one-electron steps: Hg⁰ − 1e⁻ = Hg¹⁺ − 1e⁻ = Hg²⁺, while in 0.1 M HClO₄, mercury oxidation takes place in one two-electron step. In both cases, the anodic and cathodic peak potential separation values and current and peak area ratios indicate that the redox process is quasireversible. Chronoamperometry studies suggest that initial kinetics of the Hg species at the Gr/SiC surface is governed by the three-dimensional instantaneous nucleation mechanism with a relatively high diffusion coefficient of 6.63 × 10⁻² cm²·s⁻¹. Such a behavior can be attributed to the negligibly low energy barriers for surface migration of Hg across the epitaxial graphene surface and the low number density of nucleation sites at Gr/SiC (5.59 × 10³ cm⁻²). According to DFT calculations, the reduced Hg complex interacts with graphene mainly though weak dispersive forces, also pointing out its low binding ability and high surface migration rate at room temperature. From the point of view of sensing applications, to reach high-performance Hg detection, these parameters need to be improved. Particularly, it is necessary to increase the number of electroactive sites for Hg nucleation to enhance the interaction between Hg and epitaxial graphene.