1. Introduction
Bismuth oxide (Bi
2O
3) is a semiconductor material that presents polymorphism in six different crystalline phases: α and δ (stable phases) and β, γ, ϵ, and ω (metastable phases at high temperatures) [
1,
2]. Due to its electronic properties and low toxicity, Bi
2O
3 has been used in multiple applications, such as the fabrication of gas sensors, electrochemical sensors, antimicrobial agents, and photocatalysts [
1,
3]. On the other hand, bismuth oxychloride (BiOCl) belongs to the compounds known as bismuth oxyhalides (BiOX), which are semiconducting materials with a lamellar structure. The Cl-Bi-O-Bi-Cl layered structure, along with its low toxicity at small concentrations (less than 0.5 μg/mL) [
4] and its band gap, which ranges between 3.2 eV and 3.5 eV, make BiOCl suitable for use as a photocatalyst when exposed to UV light [
5].
In recent decades, nanomaterials based on Bi
2O
3 and BiOCl have attracted significant interest from the scientific community due to their application in the photodegradation of organic pollutants. Key areas of research include synthesis methods, doping, and the morphology control of Bi
2O
3 and BiOCl nanostructures to enhance their photocatalytic activity. Ghadi et al. reported that the α and β phases of Bi
2O
3 can degrade indigo carmine (IC) and rhodamine B (RhB) under UV and visible light irradiation, with higher efficiency under UV irradiation [
6]. Furthermore, they demonstrated that an α/β-Bi
2O
3 heterojunction obtained through a solid state reaction–annealing route achieves a higher degradation rate of IC and RhB compared to the individual α and β phases of Bi
2O
3. Li et al. reported the synthesis of BiOCl nanolayers using a solvothermal method with bismuth nitrate pentahydrate (Bi(NO
3)
3•5H
2O), sodium chloride (NaCl), and ethylene glycol (C
2H
6O
2) as precursors. These nanostructures were successfully used to degrade RhB under visible light irradiation, achieving a 97% degradation of the contaminant within 20 min of exposure to visible light [
7].
Bismuth compounds can be synthesized through various methods, with the laser ablation of solids in liquids (LASL) technique being one of the most commonly used due to its versatility. LASL enables the synthesis of nanoparticles (NPs) by impinging high-power laser pulses onto a target submerged in a liquid solution. In recent years, the LASL technique has been employed to obtain a wide range of nanomaterials with minimal modifications to the experimental process. Lin et al. reported the synthesis of spherical and quasi-spherical α-Bi
2O
3 NPs via laser ablation in ethanol [
8]. These NPs demonstrated photocatalytic activity in the degradation of IC when irradiated by a commercial 365 nm LED.
On the other hand, BiOCl NPs are mostly synthesized through the hydrothermal method, using water, hydrochloric acid, sodium chloride, or bismuth chloride (BiCl
3) as precursors [
7,
9,
10]. The LASL technique provides an alternative synthesis route for this type of NPs, reducing both the synthesis time and the amount of chemical reagents used, while also allowing control over the NPs’ morphology by adjusting the laser parameters [
11]. In the literature, the use of HCl, a common precursor of the hydrothermal method, has been reported in the synthesis of spherical BiOCl NPs via LASL [
12,
13,
14]. These NPs exhibit different properties compared to those synthesized by the hydrothermal method, such as improved morphology and a reduction in their band gap value, which is a key parameter related to the photocatalytic activity of the material. Additionally, Wei et al. reported that BiOCl nanosheets exhibit photocatalytic activity on RhB degradation under visible light irradiation. This photocatalytic activity was further enhanced by decorating the BiOCl nanosheets with gold nanoparticles [
14].
It is known that NaCl, a common precursor in the hydrothermal method, has been used as a stabilizing agent in the synthesis of metal nanoparticles via the LASL technique [
15,
16]. However, to date, the use of NaCl solutions for the synthesis of bismuth nanoparticles through LASL remains unexplored. Consequently, the feasibility of employing NaCl to synthesize BiOCl NPs through LASL, as well as the impact of this precursor on the band gap value and photocatalytic activity of Bi
2O
3 and BiOCl NPs, has not yet been fully understood. The present study focuses on the synthesis of bismuth compounds nanoparticles using the LASL technique, employing a bismuth target submerged in solutions with different concentrations of NaCl. The differences in the NaCl concentration allowed for the evaluation of how this precursor influences the transformation of Bi nanoparticles into Bi
2O
3 and BiOCl NPs, which were subsequently tested for their photocatalytic activity in the degradation of rhodamine B.
2. Materials and Methods
Colloidal bismuth nanoparticles were synthesized using the LASL technique. The experimental setup is illustrated in
Figure 1a. For this experiment, a Nd:YAG laser (Q-Smart 850, Quantel, Newbury, UK) with a wavelength of 1064 nm, pulse duration of 6 ns, and operating frequency of 10 Hz was used. A bismuth target (3 cm in diameter, 0.5 cm thick, 99.9% purity) was placed into a glass container filled with 10 mL of NaCl solutions at various concentrations (0%, 3%, 11.6%, 31.6%, by weight). The laser was directed at the surface of the bismuth target using a series of mirrors. The target was kept fixed and ablated using a fluence of 0.51 J/cm
2, achieved with an energy of 324 mJ per pulse and a spot size of 0.64 cm
2. The spot size was determined by measuring the ablation mark (9 mm diameter) on the target after the experimental process. After 300 laser pulses were applied to the bismuth target, a dark brown colloidal nanoparticle suspension was produced and collected in glass containers for further characterization (
Figure 1b).
The characterization of the obtained colloids was performed without prior washing, as the small amount of ablated material made its recovery difficult after washing processes and led to a significant loss of the material of interest. The colloidal nanoparticle suspensions were stored in glass containers until the time of characterization.
The morphology of the synthesized materials was analyzed by scanning electron microscopy (SEM) using a TESCAN MIRA 3 microscope (TESCAN, Seoul, Republic of Korea) operating at 20 KV. A drop of the material was deposited onto 10 × 8 mm2 silicon substrates, and the samples were dried at room temperature for 24 h. Transmission electron microscopy (TEM) was also employed for morphological characterization, using a JEOL JEM 1010 instrument (JEOL, Tokyo, Japan) at 90 kV to examine the size of the synthesized NPs. A drop of the sample was deposited on a 3 mm diameter grid, and the liquid medium was evaporated at room temperature.
The optical properties of the synthesized materials were studied using UV–visible spectroscopy. A Thermo Fisher Scientific Genesys 10 UV–visible spectrophotometer (Thermo Fisher Scientific, Waltham, MA, USA) was used to obtain spectra in the 200 to 500 nm range for each synthesized material. UV–visible spectra were obtained on the day of ablation, as well as 3 and 28 days afterward. The UV–visible data were used to plot Tauc graphs to estimate the optical band gap of the materials.
The chemical state of the samples was analyzed using X-ray photoelectron spectroscopy (XPS) to determine the binding energies of Bi, Cl, and O in the materials. A SPECS spectrometer (SPECS, Berlin, Germany) equipped with a PHOIBOS 150 and an Al K_α X-ray monochromator was used to carry out scans of the samples, which were deposited on silicon substrates. XPS spectra were calibrated using the C 1s peak.
The crystalline phases and chemical species of the synthesized materials were characterized by Raman spectroscopy, obtaining spectra in the range of 52 to 3374 cm−1 with a 785 nm excitation source, using a Thermo Scientific equipment model, DRX2 Smart. For this analysis, a drop of each material was deposited on silicon substrates, and the liquid medium was evaporated at room temperature. The functional groups present in the synthesized materials were characterized using infrared spectroscopy with a Nicolet iS50 FT-IR spectrometer from Thermo Scientific. A drop of each sample was deposited on silicon substrates, and the liquid medium was evaporated at room temperature.
The materials synthesized in the presence of NaCl were tested as photocatalysts. The photocatalytic activity of these materials was evaluated based on the degradation of rhodamine B (10 mg/L). For sample preparation, 3 mL of synthesized material and 1 mL of rhodamine B were placed inside test tubes. Prior to conducting the photocatalysis test, the solutions were stirred in the dark for 48 h to achieve adsorption–desorption equilibrium between the rhodamine B and the synthesized materials. The test tubes were then exposed to visible light from a fluorescent lamp positioned 10 cm away. After irradiation, the samples were analyzed using UV–visible spectroscopy at intervals of 30, 60, 90, 180, and 720 min.
3. Results and Discussion
Colloidal solutions of bismuth nanoparticles synthesized in water were analyzed by UV–visible, SEM, and TEM techniques, at 7, 13, and 15 days after synthesis, respectively. A SEM micrograph of the synthesized NPs is shown in
Figure 2a. In this image, quasi-spherical morphologies with diameters ranging from 0.8 to 1.2 mm can be seen, composed of planes oriented in multiple directions.
Figure 2b corresponds to an image of the same sample, acquired by TEM at 50,000 magnifications. The same quasi-spherical structures composed of nanosheets oriented in multiple directions are visible, along with structures smaller than 100 nm in diameter, distributed around the larger morphologies. In both images, the larger-sized structures correspond to morphologies called nanoflowers, which can be associated with oxidized bismuth nanoparticles forming bismuth carbonate ((BiO)
2CO
3). Layered structures similar to the ones observed in
Figure 2 are typical for bismuth carbonates synthesized by laser ablation of Bi in water [
17].
Figure 2c shows the optical absorbance of bismuth NPs. The inset in
Figure 2c provides a close-up view of the 200-300 nm range of the plot. In this inset, bands can be observed at 237 and 285 nm, which correspond to the presence of Bi and (BiO)
2CO
3 NPs, respectively [
12,
17].
The oxidation of bismuth nanoparticles in the presence of NaCl was monitored using UV–visible spectroscopy. The results are shown in
Figure 3a. At a 3% NaCl concentration, a band at 239 nm and a shoulder at 271 nm were observed, corresponding to the presence of Bi NPs and Bi
2O
3, respectively [
12]. As the NaCl concentration increased, bands associated with BiOCl emerged, while bands associated with Bi NPs disappeared [
12].
Figure 3b shows the Tauc plot of the synthesized materials. The Tauc plots show band gap values of 3.05 eV, 2.99 eV, and 2.84 eV for materials synthesized with 3%, 11.6%, and 31.6% NaCl, respectively. These values are associated with the presence of Bi
2O
3 and are lower than the band gap values for BiOCl [
14,
18]. The Tauc plots indicate that the optical transitions of the synthesized materials are dominated by the direct transition of Bi
2O
3, making it difficult to observe the indirect transition corresponding to BiOCl. Contrary to expectations, no proportional coefficient was found between NaCl concentration and changes in the band gap value. This may be due to differences in the composition and morphology of the synthesized materials that could modify their optical band gap.
The SEM and TEM micrographs of the four samples were obtained 28 days after the synthesis process. The SEM and TEM images of the samples synthesized with 3% NaCl are shown in
Figure 4. The SEM micrograph, presented in
Figure 4a, shows that the morphology of the synthesized material consists of quasi-spherical structures with a diameter smaller than 100 nm, which are grouped in clusters. The TEM image (
Figure 4b) shows that the smallest particles in the sample have diameters raging form 10 to 50 nm. These nanoparticles are grouped to form quasi-spherical structures and clusters, as observed in the lower-left corner of the micrograph. Spectroscopic analysis identifies the morphologies observed in
Figure 3 as α-Bi
2O
3 nanoparticles. These nanoparticles do not have morphological similarities with the (BiO)
2CO
3 nanoflowers present in the sample synthesized without NaCl, suggesting that NaCl influences the size and morphology of the NPs.
The morphology of the sample synthesized with 11.6% NaCl is shown in
Figure 5. This sample consists of clusters of quasi-spherical particles, named nano-cottons. The diameter of the nano-cottons ranges from 200 to 250 nm, as observed in the SEM micrograph (
Figure 5a). In contrast, the TEM micrograph (
Figure 5b) reveals smaller particles, with diameters less than 50 nm. Spectroscopic analysis determined that this sample consists of both α-Bi
2O
3 and BiOCl. The structures observed in
Figure 5 are identified as α-Bi
2O
3 nano-cottons, given the higher abundance of α-Bi
2O
3, compared to BiOCl in this sample, as well as the similarity of the nano-cottons to the NPs clusters in the sample synthesized with 3% NaCl.
The sample synthesized with 31.6% NaCl presents crystalline clusters of sodium chloride, as shown in
Figure 6a, which do not allow the identification of smaller structures in the observed area of the sample. The TEM micrograph of the sample (
Figure 6b) shows a structure with irregular morphology and dimensions of 150 × 300 nm
2. This sample does not exhibit morphological similarities with the nanostructures observed in the samples synthesized with 3% and 11.6% NaCl, suggesting that these irregular structures could correspond to BiOCl.
Figure 7 shows the X-ray emitted photoelectron spectroscopy (XPS) survey spectra of the four samples. In these spectra, signals corresponding to Bi 4f, Cl 2p, and O 1s can be identified, in addition to Si 2p and Na 1s signals from the substrate and precursor.
The high-resolution spectra for the Bi 4f region are shown in
Figure 8. The sample synthesized with 3% NaCl exhibits peaks at binding energies of 159.7 and 165.2 eV, corresponding to the Bi 4f 7/2 and Bi 4f 5/2 levels, respectively. Two additional lower-intensity peaks are centered at 158.8 and 164.1 eV, indicating the presence of Bi
2O
3 [
18]. The sample synthesized with 11.6% NaCl shows two peaks associated with the presence of Bi
2O
3 at binding energies of 158.8 and 164.1 eV. Lower-intensity peaks at 160 and 165.25 eV correspond to BiOCl [
10,
11]. The spectra of the sample synthesized with 31.6% NaCl shows four peaks. The peaks at binding energies of 158.3 and 163.6 eV are associated with Bi
2O
3, while lower-intensity peaks at 159.8 and 165.2 eV correspond to BiOCl.
Figure 9 shows the high resolution XPS spectra in the Cl 2p region. The sample synthesized with 3% NaCl exhibits peaks at 202.3 and 203.7 eV, corresponding to the Cl 2p 3/2 and Cl 2p 1/2 levels, respectively. None of these peaks are associated with Bi-Cl bonds. The sample synthesized with 11.6% NaCl shows four peaks in its high-resolution spectra, with binding energies of 199.2 and 200.8 eV, characteristic of the Cl
- ion in BiOCl molecules [
19]. In the sample synthesized with 31.6% NaCl, the peaks at binding energies of 198.6 and 200.2 eV correspond to BiOCl.
The O 1s spectra are shown in
Figure 10. The sample synthesized with 3% NaCl shows two peaks at binding energies of 530.5 and 532.1 eV. The peak at 530.5 eV corresponds to the Bi-O interaction present in the sample [
20], while the peak at 532.1 eV is attributed to the presence of SiO
2, resulting from the interaction between the substrate and the environment [
21]. The sample synthesized with 11.6% NaCl shows three peaks at 530.6, 532.2, and 533.5 eV. The peaks at 530.6 and 532.2 eV correspond to the Bi-O interaction and the SiO
2 presence, respectively. The peak at 533.5 eV is associated with the presence of -OH radicals in the material [
22]. The high-resolution spectra of the sample synthesized with 31.6% NaCl shows three peaks at 529.8, 531.4, and 532.5 eV, corresponding to the Bi-O interaction, as well as the presence of SiO
2 and -OH radicals in the sample, respectively.
As the NaCl concentration increases, the intensity difference between the peaks associated with Bi2O3 and the additional peaks at the Bi 4f level increases, indicating the influence of NaCl on compound formation. In the case of the sample synthesized with 3% NaCl, peaks with binding energies potentially related to the presence of BiOCl are observed at the Bi 4f and O 1s levels; however, the Cl 2p level does not show signals corresponding to Bi-Cl bonds.
The results of Raman spectroscopy are shown in
Figure 11. At a 3% NaCl concentration, small bands are observed at 73, 93, 106, 125, and 156 cm
−1, which are associated with the presence of α-Bi
2O
3 [
11,
23]. As the NaCl concentration increases to 11.6%, the Raman spectrum changes: the band at 156 cm
−1 disappears, and a new band appears at 138 cm
−1, corresponding to the presence of BiOCl [
12,
24]. Unlike the UV–visible analysis, none of the Raman spectra show characteristic bands of Bi NPs, which may be attributed to the time elapsed between synthesis and the Raman spectroscopy analysis, allowing the complete oxidation of the bismuth. It is also observed that as the NaCl concentration increases, the presence of bands associated with BiOCl also increases.
Although additional techniques, such as XRD and EDS, could provide complementary insights into the crystalline phases and composition of the synthesized materials, the limited sample quantity made proper preparation for XRD characterization challenging. Therefore, XPS and Raman spectroscopy were selected as the primary characterization methods, as they are sufficiently sensitive to identify the sample composition and the vibrational modes corresponding to Bi2O3 and BiOCl. XPS measurements provided reliable data on the oxidation states of the elements, while the sensitivity of Raman spectroscopy to the vibrational modes of BiOCl effectively confirmed its presence. While these techniques have been adequate for the objectives of this study, we acknowledge that a more comprehensive structural and chemical characterization using XRD and EDS, respectively, could further strengthen the conclusions. These characterizations will be considered in future studies, especially as larger sample quantities become available, and thorough washing is performed to eliminate potential NaCl residues.
Figure 12 shows the FT-IR spectra of the synthesized materials. All spectra share a common band, between 527 and 528 cm
−1, which is attributed to the vibration of Bi-O bonds [
25,
26]. The FT-IR spectra of the materials synthesized with 11.6% and 31.6% NaCl show bands indicating the presence of O-H and H-O-H bonds, associated with the hydration of the samples at the time of analysis. These bands are observed in the ranges of 3404-3430 cm
−1 and 1624-1630 cm
−1, respectively. As the NaCl concentration increases to 31.6%, a band at 1401 cm
−1, corresponding to the vibration of Bi-Cl bonds, becomes apparent [
27]. The presence of Bi-Cl bonds confirms the formation of BiOCl in the oxidized NPs synthesized with 31.6% NaCl, consistent with the UV–visible and Raman results. The FT-IR analysis does not confirm the presence of BiOCl in the material synthesized with 11.6% NaCl, suggesting that the vibrations associated with Bi-Cl bonds in this sample are much weaker compared to those of O-H, H-O-H, and Bi-O bonds, making them undetectable by FT-IR.
The time evolution of the photocatalytic degradation of rhodamine B was analyzed by UV–visible spectroscopy. The absorbance of the samples was measured after 30, 60, 90, 180, and 720 min. After 720 min, the samples synthesized with 3% and 11.6% NaCl have a paler pink tone compared to their original color before irradiation, as shown in
Figure 13. In contrast, the sample synthesized with 31.6% NaCl exhibits a pale green tone.
Figure 14 shows the percentage of rhodamine B remaining in the samples after each irradiation period. The curve for the sample synthesized with 31.6% NaCl shows the highest degradation of rhodamine B, with a final concentration of 37.81%, in comparison to the 3% NaCl sample, which retained 80.27% of the rhodamine B.
The analysis of the graph in
Figure 14 reveals that the percentage of rhodamine B degradation increases with higher NaCl concentrations. However, the degradation percentage does not corelate with the band gap value of the samples. This may be due to the morphology of the synthesized materials, which can be modified by increasing the NaCl concentration, consequently enhancing the photocatalytic activity of the material.