1. Introduction
The issue of global ecological pollution has garnered considerable attention, as water resources are intricately tied to the survival of both humans and other living organisms [
1,
2,
3]. Nevertheless, due to industrialization, heavy metal pollution in aquatic environments not only causes ecological devastation but also poses a significant threat to human habitats, potentially resulting in public health crises [
4]. Among these heavy metal ions, Pb
2+ emerges as a particularly toxic ion capable of inflicting substantial harm to the heart, brain, and other organs in living organisms when present in concentrated forms [
5]. Nevertheless, ensuring environmental safety and mitigating the biological harm caused by the accumulation and non-degradability of heavy metal ions remains a daunting task for the global community.
Traditional heavy metal detection strategies, such as inductively coupled plasma mass spectrometry (ICP-MS), high-performance liquid chromatography (HPLC) and atomic absorption spectrometry (AAS), are widely recognized and employed extensively due to the benefits of extensive linearity, remarkable sensitivity and low detection limits. However, these sensing technologies demand substantial operational expertise and a considerable testing time [
6,
7]. In recent years, fluorescence and colorimetric methods have emerged as cutting-edge technologies for visually detecting heavy metal ions with specific targeted sites. However, one of the primary problems lies in the limited detecting range of targeted heavy metals [
8,
9,
10,
11]. Alternatively, the electrochemical sensor addresses this challenge by depositing the targeted ions on the electrode surface and inducing an electrochemical reaction of dissolution in the electrolyte under an applied potential. This reaction generates a distinct peak redox current, enabling the precise detection of the target substance [
3,
12,
13]. Owing to its convenience, cost efficiency and remarkable precision, this detection strategy has garnered significant attention in the field of heavy metal detection [
14]. Furthermore, electroanalytical techniques offer adequate sensitivity, miniaturized and portable equipment and satisfactory accuracy and precise performance [
15,
16]. By employing conventional techniques such as spin coating and droplet-drip**, it is feasible to achieve the desired modifications on the electrode surface. Viviana et al. [
17] proposed a synthetic approach for constructing carbon nanodots derived from biomass-based carbon materials. The modified electrode exhibited high stability and adsorption properties, enabling the electrochemical detection of heavy metal ions such as lead and cadmium ions. The conventional electrode modification method results in the degradation of the optimal performance of the working electrode due to interfacial adhesion [
18]. Taking into account the robust, sensitive and selective characteristics of metal–organic frameworks (MOFs) for the targeted metal ions, a rapid electrochemical detection of diverse heavy metal ions has been reported using the MOFs as electrode materials [
19,
20]. Nevertheless, MOF materials on the surface of the glass carbon electrode over time compromise detection performances.
To address these limitations, in situ growth on the electrode surface was carried out and directly applied to detect heavy metal lead ions without interfacial adhesion. Wang and colleagues constructed a flexible nickel-doped WO
3/CC (carbon cloth) electrode for glucose detection based on in situ synthesis, and the hierarchical microsheets of WO
3 exhibited a substantial specific surface area, greatly enhancing the rate of electron transfer [
21]. Gao et al. [
6] presented a cupric ion-sensing electrode, featuring the in situ growth of porous rod-like tungsten oxide assembled onto stainless steel mesh, which demonstrated impressive detection capabilities and promising practical applications. Shao et al. [
22] illustrated a molybdenum oxide adsorbent with mixed valence, exhibiting selectivity for silver detection and recovery in wastewater. Therefore, the process of in situ synthesis can significantly enhance the stability and reproducibility for the electrochemical detection of heavy metal ions.
Metallic nanomaterials, thanks to their minute size, extensive specific surface area, and exceptional electrical conductivity, could significantly enhance the sensitivity and linearity of electrochemical detection. Bismuth nanoparticles, among various metal particles such as gold and silver nanoparticles, exhibit superior cost effectiveness, environmental friendliness and resistance to oxygen, as well as low toxicity, positioning them as a promising candidate for the electrochemical detection of highly toxic mercury [
3]. With the assistance of the electrochemical plating method, Jiang et al. designed and fabricated an integrated and wearable detecting platform by printing bismuth films, and this platform was successfully utilized for the real-time detection of heavy metal ions [
23] Feng et al. [
24] successfully achieved remarkable stability and sensitivity in measuring trace amounts of lead ions by employing nitrogen-doped carbon nanosheets encapsulating bismuth nanoparticles (Bi@NC). The porous carbon composite, co-doped with Bi/Bi
2O
3, was derived from a bismuth-based organic framework, offering a wide linear range for the electrochemical detection of lead ions. Notably, the sensor exhibited exceptional stability, reproducibility and satisfactory selectivity [
25].
In this work, an electrochemical sensor based on Bi/Ag@CC electrode material was constructed and applied to the detection of Pb
2+ in tap water and lake water samples. The introduction of Ag nanoparticles significantly enhanced the conductivity of the sensor, which was achieved through a simple solution-based synthesis method. Additionally, a Bi layer was deposited on the surface of Ag@CC using an electrochemical deposition approach. The integration of Bi with Ag improved both the electrochemical activity and acid resistance of the sensor. Furthermore, the carbon film serving as a support skeleton not only ensured high electrical conductivity and rapid electrochemical kinetics but also effectively mitigated volume changes during the detection of heavy metal ions [
26]. Finally, the Bi/Ag@CC composite was employed as an electrochemical detecting electrode material for Pb
2+ sensing using the DPV mode, demonstrating excellent electrochemical performance and electrocatalytic behavior towards heavy metal ions.
2. Materials and Methods
2.1. Materials
All chemicals used to measure heavy metal ions were of analytical grade. Silver nitrate (AgNO3), ascorbic acid, lead nitrate (Pb[NO3]2), bismuth nitrate (Bi[NO3]3), potassium ferricyanide (K3Fe[CN]6), potassium chloride (KCl) and standard solutions of 1 mg/mL Pb in 2% nitric acid were obtained from Aladdin Chemical Reagent Co., Ltd. (Shanghai, China). The carbon cloth was purchased from Keshenghe (W0S1011, Shenzhen, China). Deionized water was prepared by our own lab equipped with a Flom ultrapure water system (18 MΩ·cm). All the chemicals were utilized directly without further purification.
2.2. Preparation
Carbon cloth as a substrate was firstly soaked and cleaned with acid solution, ethyl alcohol and deionized water, respectively. After drying, the carbon cloth was cut into the size of 20 mm × 10 mm × 1 mm. The carbon cloth was soaked in 0.1 mM AgNO3 for 20 min and then dried. Next, the dried carbon cloth was added into the 0.2 mM ascorbic acid solution for 10 min, leading to the reduction of Ag nanoparticles, which was named Ag@CC. The Bi/Ag@CC electrode was synthesized via an electrochemical deposition process. The deposition potential and time were selected to be −0.9 V and 480 s, respectively, and the concentration of Bi(NO3)3 was 0.2 g/L. Then, the dried samples were named Bi/Ag@CC electrodes. For the Bi@CC electrode materials, the preparation process remains identical to the aforementioned procedure, with the exception of the absence of the in situ reduction of silver nitrate solution.
2.3. Morphological Characteristics
The scanning electron microscopy (ZEISS, GeminiSEM 300, Jena, Germany) with an accelerating voltage of 3 kV was applied to observe the morphology of the prepared electrodes and EDS elemental map** images. And, the crystal structure of samples was recorded by an X-ray diffractometer (XRD, Tongda, Hong Kong, China) with a scanning speed of 5° min−1. X-ray photoelectron spectroscopy (XPS, PHI QUANTERA-II SXM, Waltham, MA, USA) was used to analyze the elements and valence states of the catalysts. The electronic conductivity was measured by a digital multimeter (RIGIOL, Bei**g, China).
2.4. Electrochemical Characteristics
The electrochemical performances were measured via the electrochemical workstation (CHI-760E, CHI Instruments, Shanghai, China) with a conventional three-electrode system. The counter electrode, reference electrode and the working electrode were the graphite rod, Ag/AgCl electrode and the prepared electrodes, respectively. To mitigate the impact of extraneous ions on the accuracy of measurement results, the electrolyte solution employed in this study is a standardized lead nitrate solution. And, the pH of the electrolyte was adjusted by the acidic and basic solutions. Differential pulse voltammetry (DPV) was used by scanning from −1.0 V to −0.2 V, and the pulse height was set as 50 mV. The pulse amplitude and pulse time were set by the instrument without change. And, the scanning rate was adjusted during the experimental measurements. The deposition voltage and time were −1.2 V and 360 s for the preconcentration of heavy metal ions, respectively. The cyclic voltammetry (CV) with a measurement range of −0.6 V~0.6 V and the electrochemical impedance spectroscopy (EIS) at the frequency range of 0.01 Hz to 100 kHz were tested. All the tests were conducted at room temperature.