In this work, we have improved an eco-friendly, pure, nontoxic method, for the generation of CuO NPs using the B. ciliata rhizome extract. (Fig. 1.). B.ciliata is widely used in traditional medicine because of its phytochemicals (bergenin, gallic acid, (+) - catechin, paashaanolactone etc.) [45, 46]. CuSO45H2O, initially metal precursor, reacts with the hydroxyl ion in water to form copper hydroxide. The phytochemicals contained in the B. ciliata extract are used as reducing and stabilizing. Copper oxide nanoparticles are synthesized from copper hydroxide with these phytochemicals.
4.1 Characterization of nanoparticles
The first step in the characterizing of nanoparticles is the color transformation of solution (Fig. 2.) indicates the reduction of copper ions into CuO NPs using aqueous extract of B. ciliata. It occurs because of visual color change of solution from light brown to brick red (brownish), which is due to the excitation of surface plasmon vibrations in CuO NPs [47].
UV–Visible absorption spectrum was used for the analysis of optical properties of CuO NPs. Surface plasmon absorption of metal oxide generated an absorption peak at 260 nm in the spectrum. No additional peaks were found in the range of 200–500 nm, and the absorption peak was found to be symmetric. (Fig. 3a.). The results were in good agreement with study of Kumar et al [48]. Surface plasmon absorption and collective oscillation of free conduction band electrons stimulated by electromagnetic radiation are achieved in metal oxide nanoparticles. If the wavelength of the incident light is greater than the particle diameter, a resonance will occur. Surface plasma resonance absorbance is very sensitive to the size and shape of the particles, their distance between particles, the surrounding environments and nature [49]. In the range of 4000–400cm1, the FTIR spectrum was measured in solid phase using the potassium bromide pellet technique. (Fig. 3b.) gives information about the spectral peaks proposing, the occurrence of bands relevant to amide N- H stretching (3402 cm− 1), amide C = O stretching (1578cm− 1), alkanes C = O stretching (2350cm− 1), nitro N-O bending (1399 cm− 1). The presence of CuO NPs band at 618 cm− 1 accepted to the vibrations of Cu-O. The above result confirms that the bio-active compounds present in the B. ciliata rhizome extract have upper hand in the production of CuO NPs. The little diversity in the peak position from original bonding show that the some of the metabolites (tannins, flavonoids, alkaloids, and carotenoids etc) are plenty in the bud extract that can produce the CuO NPs [50].
XRD analysis is used to determine the crystalline properties of NPs. In this work, XRD analysis of CuO nanoparticles obtained by green synthesis is shown in Fig. 4a. small different diffraction peaks at 32.80, 39.75, 61.40 and 71.02, that indexed the planes 111, 200, 220 and 311 of face centered cubic structure of CuO NPs with a monoclinic phase (JCPDS- 87–0717). CuO nanoparticles synthesized from B. ciliata rhizome extract have been shown to be crystalline in nature by XRD analysis and no other phase showing the purity of these nanoparticles has been observed. The Debye-Scherrer equation was used to measure the crystal size of the nanoparticles obtained [51–53]:
D = Kλ/βcosθ
K: Scherrer’s constant (K = 0.94), D: crystalline size, k: X-ray wavelength (0.1546 nm), b: fullwidth at half-maximum of the XRD line in radians, h: half diffraction angle.
The average size of CuO NPs was measured be about 20 nm. The XRD data of the bio-synthesis CuO nanoparticles obtained in previous studies are parallel to the CuO nanoparticle data obtained in this study [37, 54]. DLS analysis was used to measure the average particle size (Fig. 4b). The average particle size of the CuO NPs obtained accordingly is less than 50 nm. Figure 5.a shows the SEM analysis of CuO NPs synthesized from B. ciliata. According to this SEM analysis, particles appear spherical and hexagonal, but there are also large particles formed by the combination of small particles. EDS analysis of CuO NPs synthesized by B. ciliata is given in Fig. 5.b. According to this analysis, elemental Cu is at a highly intensive important peak of elemental Cu and O with the atomic 71.8% of and 28.23 % which is in suitability with the main description line of metallic CuO NPs.
Consecutive increase in redox reaction i.e., oxidation as well as reduction peaks were observed with increasing scan rate potential. Observing cathodic current peaks i.e., 15µA at 20mV/cm, 28µA at 40mV/cm, 40µA at 60mV/cm and 60µA at 100mV/cm, indicating increased amount of catalytic activity due to presence of green synthesized CuO nanoparticles. A linear plot between scan rate vs. cathodic current peaks has been indicated in Fig. 6. Scan rate range from 20mV to 100mV were used. Increase in scan rate corresponded to increase in cathodic current suggesting CuO NPs electrode reduction is exclusively diffusion-controlled electron transfer [55] and exhibit a strong linear relationship with a R2 value of 0.9871.
4.2 Antioxidant Activity
Both the crude plant extract and the NPs were tested for phenolic and flavonoid content. Phenol content of BC was found to be 35.02 1.23 mg GAE / mg. In CuO NPs synthesised from the extract, this quantity is 49.23 1.66 mg GAE / mg. The bound flavonoid content of CuO NPs was measured (22.08 1.04 mg of QE / mg). In our sample, the B. ciliata extract contained 30.09 1.28 mg of QE / mg flavonoid material. (Fig. 7 and Table 1).
Antioxidants are compounds that prevent the oxidation of essential biological macromolecules by inhibiting the propagation of the oxidizing chain reaction. The antioxidant activity of biogenic synthesis of CuO NPs was assessed using the DPPH, ABTS, and FRAP scavenging assays, which showed that a compound's reducing power is directly proportional to its antioxidant activity. CuO NPs is found to have antioxidant properties. ABTS assays the CuO NPs (IC50 = 72.4 g/mL) and FRAP assays the CuO NPs (IC50 = 109.0 g/mL) for DPPH, CuO NPs (IC50 = 91.2 g/mL), and FRAP assays the CuO NPs (IC50 = 109.0 g/mL) (Fig. 7c and 7d). For the DPPH, ABTS, and FRAP assays, Ascorbic acid was used as a norm, with IC50 values of 29.24, 28.7, and 26.3 g/mL, respectively. These study reveals that Bergenia ciliata CuO NPs are more effective at scavenging free radicals and can be used as a major antioxidant source in antioxidant-based therapies. The CuO NPs' scavenging behaviour increases as the sample concentrations increase. As compared to other green synthesised nanoparticles, the presence of proteins and amino acids, as well as carbohydrates, flavonoids, glycosides, phenolic compounds, saponins, and tannins, results in higher operation. Lower the IC50 value, greater is the hydrogen donating potential of the free radical scavengers and thus their antioxidant activity.
Table 1
Antioxidant activity of BC and CuONPs.
IC50 value (µg/mL) |
Sample | ABTS | DPPH | FRAP |
BC | 138.0 | 135.2 | 144.1 |
CuO NPs | 91.25 | 72.4 | 109.0 |
AA | 28.73 | 29.24 | 26.3 |
4.3 Antimicrobial activity
Nanoparticles have larger surface areas compared to large particles. This large surface area interacts more with microorganisms, providing a high amount of antimicrobial effects. Copper, which has been used as an antibacterial factor for a long time, has a high antibacterial effect by 99.9% [56]. The antimicrobial effect of CuO nanoparticles, which were synthesized by performing various optimizations, was investigated. According to the results of the agar well diffusion assay, the antimicrobial activity of 20 mg / mL CuO nanoparticles is effective against food pathogens. Results revealed that the CuO NPs was better effective against all two Gram positive as compare to Gram negative bacterial strains shown in Fig. 8 and Table 2. On the basis of these observations, it can be concluded that synthesised CuONPs had strong antibacterial activity against bacteria belonging to both Gram classes. CuO NPs have an important antibacterial property due to their large surface area, which helps them to make closer contact with microorganisms. By cross-linking within and between nucleic acid strands, copper ions released later can bind with DNA molecules, causing helical structure disorder. Biochemical processes are often affected by copper ions in bacterial cells. [57, 58]. The exact mechanism behind is not known and needs to be studied further. Furthermore, the Gram negative bacteria seemed to be more resistant to CuO NPs than Gram positive bacteria. It was earlier reported that the interaction between Gram positive bacteria and nanoparticles was stronger than that of Gram negative bacteria because of the difference in cell walls between Gram positive and Gram negative bacteria. BC and CuO NPs were used to inhibit the growth of test organisms as described. The minimum inhibitory concentration (MIC) was found to be 6.25 µg/mL against S. aureus, B. subtilis, S. typhi and 25 µg/mL against E. coli (Table 3).
Table 2
Zone of inhibition of CuO NPs against various pathogenic bacterial strains.
Bacterial Strains | Samples | Positive control (Ampicillin-100 mg/mL) | Negative control (dw) |
BC | CuO NPs |
S. aureus | 13.5 ± 0.50 | 17.8 ± 0.41 | 23.8 ± 0.76 | ND |
B. subtilis | 12.2 ± 0.68 | 15.8 ± 0.76 | 25.6 ± 1.58 | ND |
S. typhi | 10.3 ± 0.72 | 15.0 ± 1.02 | 23.3 ± 0.57 | ND |
E. coli | 7.5 ± 0.50 | 11.5 ± 0.50 | 25.6 ± 0.57 | ND |
Table 3
Minimum Inhibitory Concentration of BC and CuO NPs various pathogenic bacterial strains.
MIC (µg/mL) |
S.No. | Bacteria | BC | CuO NPs |
1 | S. aureus | 25 | 6.25 |
2 | B. subtilis | 25 | 6.25 |
3 | S. typhi | 25 | 6.25 |
4 | E. coli | 50 | 12.5 |
4.4. Photocatalytic degradation
Figure 9 depicts the dye degradation mechanism followed by CuO NPs. Sharma and Dutta reported that hydroxy radicals were the most important reactive oxygen species that caused degradation when CuO NPs were used [59]. CuO NPs have been widely used as catalysts in photocatalytic degradation and reduction of contaminants [60]. Matter of fact, dark adsorption is initial step and one of the most critical aspects of the photocatalysis mechanism [61]. CuO NPs were used to study the photo degradation of cationic dyes like MB and MR when exposed to sunlight. In the presence of light radiation, the MB and MR solutions were stirred in the dark for 1 hour to establish adsorption–desorption equilibrium between the CuO NPs and dye molecules. A UV–vis spectra was then used to estimate the MB and MR concentrations. Within 135 minutes, the photocatalytic activity of B. ciliata rhizome extract mediated CuO NPs and the absorption peaks at 625 and 525 nm decreased, comprising MB and MR dye. The morphology, crystalline structure, and dimensions of NPs all play a role in photocatalytic activity, according to the literature [62]. Control experiments were carried out in the dark (both with and without CuO NPs) to rule out any possibility of dye self-degradation, dye adsorption, or NP catalytic activity in the dark. In the absence of CuO NPs, we observed negligible dye degradation after the experiment was completed (Fig. 9c and 9d). Similarly, CuO NPs had a negligible effect on dye degradation in the dark. As a result, it was determined that the dyes did not degrade significantly in dark conditions. Furthermore, dye degradation experiments in the absence of a catalyst revealed negligible dye degradation. MB and MR, on the other hand, were nearly fully degraded under direct sunlight in the presence of catalyst. These researches demonstrated that a photocatalytic mechanism was responsible for dye degradation. Sunlight is a very important factor from industrial perspective. The degradation was 55, 47%, for MB and MR dyes, respectively within 75 min of photo irradiation. While it was 92%, 85% for MB and MR dyes, respectively within 135 min of photo irradiation. After 3 hours of irradiation, an efficiency of 92 percent and 85 percent is obtained, indicating that integrating CuO NPs species into the solution serves a primary function in the improvement of photodegradation, as shown (Fig. 9e). The degradation of MB dye was observed higher as compared to MR dyes. It has been reported that the catalytic activity of a nano-catalyst is strongly influenced by the morphology and size of nanoparticles, as well as process of energy transfer, photo-generated carriers generation and consumption [63]. Balgude et al. used Sn3O4 nanoparticles to demonstrate the same form of degradation of MB dye within 60 minutes under sunlight irradiation [64]. Under UV light irradiation, Sonia et al. (2015) degraded the MB dye in 180 minutes using CuO nanoparticles [65] .
Table 4
Comparative assessment of dyes degradation efficiency using different photocatalysts
NPs | Dye | Catalyst concentration | Dye concentration | Time (min) | % degradation | Reference |
CuO | Congo red | 1mg/mL | 10 mg/L | 60 min | 90 | [66] |
Nile blue (NB) | 40 ppm | 1 mg/mL | 120 min | 93 | [67] |
ZnO | MV6B | 0.50 g | 100 mL | 210 | 68 | [68] |
Reactive black 5 | 3 g/L | 496 mg/L | 60 min | 60 | [69] |
CuO | MB | 20 ppm | 10 mg/mL | 135 min | 92 | Present study |
MR | 20 ppm | 10 mg/mL | 135 min | 85 |
Mechanism
Figure 10 illustrates the mechanism for photocatalytic activity. By generating holes in the valence band, a source of light induces electrons to excite from the valence to the conduction band. The photocatalyst holes oxidise the H2O molecules in the reaction sample to more reactive OH radicals. Owing to the presence of excited electrons in the CB, the oxygen molecule gets reduced to O− 2 radicals, and H2O2 gets reduced to OH radicals. The oxidative decomposition of dye to CO2, H2O, and other mineralization products can be caused by the oxide and hydroxyl radicals formed by CuO nanoparticles [70–73].