1. Introduction
In Europe, deep geological disposal is the preferred option for nuclear waste management to isolate radioactive waste from human environments. In France, the planned deep geological disposal facility for high-level and intermediate-level long-lived radioactive waste, known as “Cigeo”, will be constructed 500 m underground in the Callovo–Oxfordian geological formation (Cox). Overseen by the French National Radioactive Waste Management Agency (Andra), the Cox formation is a 130-m-thick stratigraphic unit primarily composed of clay, with origins tracing back approximately 160 million years. Located at depths between 400 and 600 m, this formation is a hydrogeological environment characterized by high water saturation and extremely low permeability, porosity and hydraulic conductivity.
The temperature, pH and CO
2 partial pressure of the Cox pore-water solution are constant at 25 °C, 7.3 (±0.1) and 8.10
−3 atm, respectively [
1]. Anoxic conditions prevail in the Cox formation. Within the mineralogical assemblage [
2,
3], geochemical models predict E
H values ranging from −180 to −200 mV, corresponding to an equilibrium between pyrite and pore-water sulfate [S
(+VI)] concentrations, and iron-bearing phases such as Fe-bearing carbonates or nanogoethite [
3,
4,
5,
6].
Andra is in charge of the long-term radioactive waste management in France. The radioactive wastes will be placed in horizontal pipes made of Carbon Steel API-5L-X65 (CSX65), separated from the Cox by a cemento-bentonitic filling material (CBFM). The technical specifications for developing monitoring techniques are based on the following: (i) requirements arising from the specific nature of the parameters that need to be measured in key thermal-hydraulic-mechanical-chemical and radiological (THMCR) processes; and (ii) requirements related to the minimum accuracy and long-term stability of the monitoring methods—considering that there will be little or no access for re-calibrating the sensors—for accurately monitoring the evolution of the near-field around the radioactive waste, including Cox pore water alone and in contact with carbon steel CSX65 and an alkaline CBFM (pH > 11.7).
Some constraints specific to on-site conditions must be considered for developing the sensors [
7]:
The wide range of redox potentials over the Pourbaix diagram due to the following: (i) gas emissions such as O2 from excavation, H2 from the release of radioactive waste and metal corrosion, CO2 from organic-matter degradation, H2S from the activity of sulfate-reducing bacteria (SRB), or CH4 from the activity of methanogenic bacteria; (ii) sulfide (HS−/S2−) production due to the activity of SRB.
The temperature will increase due to radioactive disintegration (25 °C ≤ T ≤ 90 °C).
The initial pH of the Cox pore water will decrease due to pyrite oxidation. Then, a progressive alkalization of the Cox pore water will occur due to its contact and interaction with CBFM (pH greater than 11.7). Thus, the pH domain to monitor ranges from 4.0 to 13.0.
The two key parameters for monitoring the above parameters are thus pH and redox potential [
8] as they effectively reflect physical, chemical and electrochemical (redox) transformations. To ensure the safety and reversibility of the nuclear waste storage, reliable sensors are essential for monitoring changes in the near-field environment [
7,
9,
10]. The objective is to design, create and optimize a robust multi-parameter probe for the on-site monitoring of pH (±0.5 pH unit) and redox potential (±50 mV) in order to ensure the long-term safety of the operation [
7]. The multiplication of electrodes is essential for consistently and reliably monitoring the evolution of the aqueous environment over time. Evaluating the durability and performance of these sensors requires testing under conditions that replicate real-world scenarios, such as using a glove box to simulate low oxygen controlled atmosphere and, additionally, to investigate the impact of sulfides, which may arise from bacterial activity in confined environments [
7].
The glass electrode is the most widely used pH sensor. However, it has several limitations, including fragility, lack of long-term stability, high impedance and difficulties in miniaturization for specific applications. As a result, new types of electrodes have been developed to respond to the requirements of measuring pH in different types of solutions, such as corrosive solutions, alkaline solutions and HF solutions. These innovations include ion-sensitive field-effect transistor (ISFET) pH sensors [
11,
12], fiber optic pH sensors [
13,
14,
15], hydrogel membrane pH sensors [
16,
17] and metal oxide pH sensors [
8,
18,
19].
Metal oxide sensors have attracted particular attention because of their advantages, such as fast response times and high stability. The choice of metals is mainly based on their electrochemical behavior and stability across the pH range (4–13). Several research groups have investigated new metal oxides for use as pH electrodes, including Ir/IrO
x [
20,
21,
22,
23], Pt/PtO
2 [
24,
25,
26], Ru/RuO
2 [
27] Ti/TiO
2 [
28], Sb/Sb
2O
3 [
7], Pb/PbO
2 [
29] and CeO
2 [
9].
Beyond traditional metal oxide electrodes, electrodes fully composed of metal oxides on non-metallic substrates are also used. The pH response of these electrodes is often attributed to the presence of the mixed oxide-hydroxides within the film [
30,
31,
32]. For some materials, further research is needed to develop coatings that can minimize mechanical stresses on the sensitive layer during measurements in basic environments. Electrodes such as Sb/Sb
2O
3 [
7] have been tested under controlled conditions that replicate environments likely to be encountered in storage facilities [
10].
On the other hand, molybdenum oxides also have considerable potential due to their different oxidation states. Molybdenum exhibits oxidation states from (+II) to (+VI), enabling it to form a wide range of oxide compounds [
33], a capability linked to its delocalized 4d electrons. The most important and common are molybdenum trioxides (MoO
3) and dioxides (MoO
2). The nature and composition of surface oxides vary according to the nature of the medium (air, aqueous, non-aqueous), the pH of the electrolyte, the potential of the electrode and the operating parameters, such as temperature and pressure [
33]. MoO
3 has a perovskite-type structure, with oxygen vacancies. The structure of molybdenum allows the efficient insertion or intercalation of ions like H
+ within this structure. This intercalation process modifies the optical properties of the material and its charge storage capacity. Molybdenum is therefore very useful in applications such as for batteries and electrochromic devices [
34].
However, the use of molybdenum is still relatively limited for pH applications compared with these more commonly used oxides (RuO
x and IrO
x). For example, Shuk et al. [
35] developed pH sensors based on molybdenum bronzes, such as Na
0.9Mo
6O
17 and Li
0.9Mo
6O
17. The Na-molybdenum-oxide bronzes pH sensors exhibited near ideal Nernstian behavior in the pH range of 3 to 9 [
35]. Another example is the molybdenum diselenide/nitrogen doped graphene oxide screen-printed electrode (MoSe
2/NGO), developed by Poorahong et al., which demonstrated high stability and reproducibility over a wide pH range from 2 to 14 [
36].
In this study, MoOx electrodes were prepared via thermal oxidation and then hydrated in milliQ water. The surface morphology and chemical composition of the MoOx films were studied using SEM-EDS and XPS. In addition, the influence of hydration on the evolution of the E–pH relationship of the electrodes was analyzed and compared. Electrochemical performance of the electrodes, as pH sensors, was evaluated under calibration conditions simulating field expectations. Their reliability and robustness were assessed through electrochemical measurements at 25 °C, under atmospheric pressure and/or in a glove box (GB).
2. Materials and Methods
2.1. Sample Preparation
Molybdenum wires (diameter 1.5 mm, purity 99.9%, Merck, Rahway, NJ, USA) were used. The wires were polished with a series of abrasive papers (1000#, 1500# and 2000#) for around 2 min to remove the surface oxide layer. Next, the wires were ultrasonically cleaned in milliQ water (resistivity = 18.2 MΩ·cm) and ethanol, respectively. Then, the cleaned molybdenum wires were oxidized at 500 °C for one hour. After cooling to room temperature, the wires were rinsed again with milliQ water. For electrode fabrication, one end of the oxidized molybdenum wire was affixed to a copper conductor via soldering. The connection was subsequently insulated using heat-shrink tubing, ensuring that precisely 3 mm of the oxidized molybdenum surface remained exposed for electrochemical interaction. The electrodes were then immersed in milliQ water at 25 °C for hydration, as shown in
Figure 1.
2.2. Supporting Electrolytes: Buffers and Solutions
Experiments were conducted at a constant temperature of 25.0 ± 0.1 °C, either at atmospheric pressure or within a thermo-regulated glove box (pN
2 = 1 atm, PO
2 ≈ 10
−6 atm) [
7]. The electrodes’ responses to pH variations were extensively examined by immersing them in various buffered solutions prepared using deionized water with a resistivity of 18 MΩ·cm. Each buffered solution had an ionic strength of 0.05 M, achieved by adding a precise amount of NaCl to closely match the ionic strength and salinity of the in-situ Cox pore water [
6]. For pH > 10.8 (the upper limit of carbonate-based buffers), the pH of the solutions was adjusted by adding 1 M sodium hydroxide. Specific buffered solutions used, along with their corresponding effective pH ranges, are outlined in
Table 1. In all experiments investigating the influence of pH on the open circuit potential of the electrodes, measurements were conducted within a pH range between 4 and 13.
In addition to the calibration curves constructed in the absence of sulfides, we performed calibration curves in the presence of sulfides at various concentrations (ranging from 10−7 to 10−3 M). Sulfides exist in various forms: H2S(g), H2S(aq) and HS−(aq), S2−(aq). The speciation of sulfides in solution depends on the pH value. Since the pH of the Cox pore water is close to neutral (7.0 < pH < 7.4 at 25 °C), sulfides will predominantly be in the form of H2S(g), H2S(aq) and HS−(aq). It is crucial to consider the expected pH variations during the operational phase of the storage facility, as they will impact sulfide speciation. This is why we decided to investigate the electrode behavior in the presence of sulfides at various concentrations and pH values in the laboratory.
2.3. Characterization of MoOx/Mo Film
2.3.1. Scanning Electron Microscopy (SEM)
The morphology of MoOx/Mo coatings was observed with a TESCAN (Tescan Group, a.s., Brno, Kohoutovice, Czech Republic) scanning electronic microscope (SEM) with an operating energy of 15 kV, coupled with energy dispersive X-ray spectroscopy (EDS) to characterize the elemental composition.
2.3.2. X-Ray Photoelectron Spectroscopy (XPS)
The XPS spectra were recorded by a Thermo Fisher Scientific (Courtaboeuf, Les Ulis, France) spectrometer equipped with an Al K alpha monochromatic high-energy radiation source (hʋ = 1486.7 eV) and a hemispherical analyzer operating in Constant Analyser Energy (CAE) mode. Additionally, the X-ray spot size measured 200 µm, resulting in an irradiated area of approximately 0.5 mm2. Binding energies were calibrated based on the C 1s peak (284.88 eV). XPS data were analyzed using CASA XPS software version 2.3.25PR1.0 (Clearwater, FL, USA). A Gaussian-Lorentzian GL (30) peak shape was employed to deconvolve the C1s and O1s peaks, while a Modified Lorentzian Peak Function LF (0.8, 1.35, 280) was used for the Mo 3d peaks. Survey scans were conducted with a pass energy of 200 eV and a step size of 1 eV. High-resolution windows were acquired with a pass energy of 50 eV and a step size of 0.1 eV.
2.4. Potentiometric and pH Measurements
The study of potential variations of Mo-MoOx based electrodes was conducted in double-walled Pyrex glass eletrochemical cells. These cells were connected to a thermostatic bath to maintain a constant temperature of 25 °C. A data acquisition unit (Keithley Instruments, model 2700, Cleveland, OH, USA), handled by a computer via KickStart version 2.7.0 software, was used to record potential variations every 15 s for 10 to 15 min. Open-circuit potential measurements of the electrodes were conducted relative to Ag/AgCl with 3 M KCl (Radiometer Analytical REF201, Hach Lange GmbH, Düsseldorf, Germany) reference electrode and were subsequently converted and referenced versus the standard hydrogen electrode (SHE). Additionally, a pH meter (OrigaMeter OpH218 from Origalys, Rillieux le Pape, France), coupled with a commercial pH electrode (OGPH203, OrigaSens, from Origalys), which was also connected to the data acquisition unit, was employed to confirm measured pH values. Data translation was facilitated by a computer.
As otherwise stated, all the experiments were made in triplicate. Each experiment had its own measurements. Regardless of the experiment, pH reached a stable value in a few seconds. OCP reached a stable potential in the range of 1 to 2 min. For each experiment, the last ten values were used to calculate the mean and the relative standard deviation of OCP and pH. For each investigated pH value, the mean and standard deviation were calculated for ten measurements repeated three times (x = 10; N = 3). We have chosen to present only the first among the three experiments in the corresponding figure and we added the statistical treatments in a separate table.
2.5. Electrochemical Impedance Spectroscopy (EIS)
The impedance of the all-solid-state MoOx/Mo electrode was measured at room temperature using a Model 2273 potentiostat–galvanostat (AMETEK, Inc., Berwyn, PA, USA), interfaced with a PC system and controlled by PAR’s PowerSuite v.2.58 software, in buffer solutions with pH values of 3.98, 6.98 and 10.8 using a three-electrode configuration. The MoOx/Mo electrode served as the working electrode, a platinum grid served as the counter electrode, and an Ag/AgCl KCl 3M electrode (Radiometer Analytical REF201, Hach Lange GmbH, Düsseldorf, Germany) served as the reference electrode. An AC voltage of 10 mV (rms) was applied, and the frequency range varied from 1 MHz to 0.1 mHz. The data were fitted using Zsimpwin 3.60 software (Echem software, Ann Arbor, MI, USA).
4. Conclusions
In this study, the morphology, chemical composition and pH sensing properties of MoOx sensors prepared via thermal oxidation and hydrated in milliQ water were investigated. SEM and EDS results indicate that a MoOx film covers the surface of the molybdenum sensor prepared via thermal oxidation at 500 °C. XPS analysis revealed that the molybdenum substrate is oxidized to Mo (VI). The hydration treatment is crucial to the stability and reliability of the MoOx sensor performance. A 70-day hydration treatment was required to achieve a stable pH response of −61 mV/pH, slightly exceeding the theoretical Nernst value. SEM and EDS analysis showed that the surface is largely covered with MoOx, with varying values of “x” at different locations.
XPS analysis after hydration confirmed the presence of Mo (IV) and Mo (VI), indicating a reduction of Mo (VI) to Mo (IV). The performance of the electrodes was studied in the presence and absence of oxygen, and in the absence of oxygen in the presence of sulfides. The absence of oxygen increased sensitivity and reduced the experimental standard potential (E0Exp), probably due to the effect of oxygen vacancies. The performance of the electrodes in the presence of sulfides showed that the sensors still performed well at low sulfide concentrations. However, at higher concentrations, the formation of complexes with sulfides can reduce electrochemical activity. The thermal oxidation method is therefore recommended for long-term pH monitoring, particularly in environments where oxygen and sulfide concentrations are variable, due to the stability and robustness of MoOx electrodes under such conditions.