1. Introduction
Bacterial resistance and multi-resistance to antibiotics is a global public health problem that is continuously growing. In the last decades, nanotechnology has contributed to possible solutions for the management of bacterial resistance to antibiotics, and with new methods for diagnosis and handling of diseases [
1,
2,
3,
4,
5]. The antimicrobial and antioxidant properties of metal and metal oxide nanoparticles (NPs) are promising for multiple applications in different areas of medicine [
6,
7,
8,
9]. It has been documented that their antibacterial effect to combat bacterial resistance to antibiotics is promising [
10,
11]. However, the cytotoxic effect on animal cells has limited the applications to combat resistant bacteria [
12,
13]. For this reason, in recent decades, alternative nanocomposites with outstanding biocompatibility, lower cytotoxicity, and immunogenicity have been sought [
14,
15].
The implementation of the biological methods, also called “green methods”, for the biosynthesis of metal and metal oxide NPs, have been extensively explored since they cause less damage to the environment, compared to chemical and physical methods, and could improve the effectivity and biocompatibility of nanomaterials [
16,
17,
18,
19,
20,
21].
The use of fungi to synthesize NPs holds particular interest, since fungi secrete large amounts of enzymes and metabolites and are easier to manipulate in the laboratory [
22]. For instance, the synthesis of metal and metal oxide NPs using fungi has been studied and reported for over two decades [
22,
23,
24]. The intracellular compounds of the fungus as well as the compounds excreted into the medium (extracellular compounds) can be successfully used to produce NPs [
25,
26]. One of the benefits of using fungi for synthesizing metal-based NPs is that they do not require reducing chemical agents, protective agents, and/or stabilizing agents, which can be toxic [
22].
For biomedical applications, silver and gold NPs have been the most studied, however NPs such as copper oxide, iron oxide and zinc oxide are currently being considered [
27,
28,
29,
30]. Recently, the production of copper and copper oxide NPs has gained interest, since in recent studies they have been shown to be useful for biomedical applications because of their anticancer, antioxidant, antimicrobial, and antidiabetic properties [
9,
18,
31,
32,
33].
In this work, copper oxide nanoparticles (CuONPs) were produced using the extract and supernatant of
Ganoderma sessile; this fungus is considered non-pathogenic to plants, animals or humans, is easy to handle and has a low production cost. Furthermore, mushrooms of the
Ganoderma genus are considered medicinal, with antioxidant, anti-inflammatory and antitumor properties [
34,
35]. In addition, it has been shown that the extract and the supernatant of liquid cultures of
G. sessile are not toxic to mammalian cell lines [
26]. Therefore, the objective of the present study was to synthesize copper oxide NPs (CuONPs) using an eco-friendly method and to determine their antibacterial properties, seeking alternative methods to combat human pathogens.
2. Materials and Methods
2.1. Strain, media and growth conditions
Ganoderma sessile was obtained from the fungal stock of the Microbiology Department (CICESE). The strain was inoculated in Petri plates with potato dextrose agar medium (PDA) and incubated at 30 °C for 96 h. Once the mycelium filled ¾ of the culture dish, 10 plugs of the mycelium were taken with a standard size of 10 mm in diameter using a sterile borosilicate tube. The plugs were transferred to 250 mL Erlenmeyer flask with 100 mL of potato dextrose broth medium (PDB), and placed in an incubator with shaking at 120 rpm for 7 days at 30 °C.
2.2. Obtention of fungal supernatant and extract
To obtain fungal supernatant, the biomass obtained from liquid cultures was washed with sterile distilled water and placed in Erlenmeyer flasks with sterile deionized water in a 1:2 proportion (w/v) and incubated at 120 rpm for 24 h at 30 °C. After 24 hours, the supernatant was obtained by filtration through a nitrocellulose membrane with a pore size of 0.45 µm (MF-Millipore) and subsequently through a nitrocellulose membrane with a pore size of 0.22 µm (MF-Millipore), to eliminate all biomass.
Fungal extract was obtained using biomass from liquid cultures in a 1:1 proportion (w/v); biomass was washed with sterile distilled water and macerated with sterile deionized water using an agate mortar. Once macerated, it was centrifuged for 15 min at 10,000 rpm at 22 °C, and finally the aqueous extract was decanted. The extract obtained was filtered as described above.
2.3 Biosynthesis of copper oxide nanoparticles (CuONPs)
CuONPs were synthesized using fungal extract and/or supernatant mixed with pentahydrated copper sulfate (CuSO4.5H2O) 5 mM (Sigma-Aldrich, St. Louis, MI, USA) as follows: Copper sulfate : fungal supernatant (S) or extract (E) were mixed in a 3:1 proportion, pH was adjusted to 10 with NaOH (10 mM), then the resulting suspension was incubated for 24 h at 60 °C.
2.4 Characterization of CuONPs
CuONPs were analyzed by UV-Vis spectroscopy at 200 to 800 nm [
32] in a Perkin Elmer precisely UV-Vis lambda/25 spectrophotometer (PerkinElmer Inc.,Waltham, MA, USA). Further characterization was carried out to determine the hydrodynamic diameter (HD), the zeta potential (ZP) and the polydispersity index (PDI) using a Zetasizer Nano ZS instrument (Malvern Panalytical Inc., Westborough, MA, USA). Nanoparticles were analyzed under transmission electron microscopy (TEM) (Hitachi H7500, Hitachi Ltd., Tokyo, Japan) at 100 kV for size and shape determination. Also, CuONPs were examined using a high-resolution transmission electron microscope (HRTEM) (JEM-2100 from JEOL, JEOL Ltd., Tokyo, Japan) operated at 200 kV. To assess mean size of NPs, the ImageJ program (free version forWindows 1.8.0_172) was used.
2.5. X-ray diffraction (XRD) Analysis of Synthesized CuONPs
The structural analysis was performed by X-ray diffraction using a Bruker D8 Advanced diffractometer equipped with Linxeye Detector. The XRD pattern were collected with Cu Kα radiation and 2θ scanning angle variation between 10° and 80°. The phase analysis was supported with PDF-2 software.
2.6. Fourier Transform Infrared Spectroscopic (FTIR) Analysis of Synthesized CuONPs
To identify the functional groups that could be participating in the formation and stabilization of copper oxide nanoparticles, the samples were centrifuged, then the precipitates were collected and subsequently lyophilized. The FTIR spectra were acquired using a Bruker Tensor 27 spectrometer with Total Attenuated Reflectance (FTIR-ATR) in a range of 4000 cm-1 to 400 cm-1 in transmittance mode.
2.7. Evaluation of Antibacterial Activity
Antibacterial activity of the synthesized CuONPs was evaluated against
Escherichia coli (ATCC 25922),
Staphylococcus aureus (ATCC 25923) and
Pseudomonas aeruginosa (ATCC 27853) as the minimum inhibitory concentration (MIC). For this, the plate microdilution assay was used, following the protocol of the Clinical and Laboratory Standards Institute [
36]. For the microdilution assay, each bacterial strain was inoculated in Petri dishes with LB agar medium at 37 °C for 24 h. Subsequently, four colonies were inoculated in Mueller Hinton broth (MHB) and incubated at 37 °C under agitation, until reaching an approximate concentration of 5x10⁵ CFU / mL [
36]. Then, the MIC determination was carried out in Polystyrene 96-Well microplates (Costar 3595). In each well, 50 µL of MHB was placed, and the different concentrations of CuONPs-S and CuONPs-E used, then 5 µL of the bacterial inoculum were added. MHB without inoculation and MHB with bacterial inoculum without CuONPs, were used as controls. The plates were incubated at 37 °C for 24 h. For the analysis, the Multiskan Sky version 1.00.55 plate reader (Thermo Scientific™) was used, with the Skanlt 6.0.1 software. After the incubation time, 10 µL of each well were inoculated in Petri dishes with LB agar and incubated for 24 to 48 h at 37 °C to determine bacterial growth (% CFU), the assays were done in triplicate.
2.8. ROS production in bacteria
To evaluate the production of reactive oxygen species (ROS) in bacteria, the following protocol was carried out: in a 96-well plate cells were seeded at 1×105 cells per well, and exposed to different CuONPs concentrations (19.9, 9.95, 4.97, 2.48, 1.24, 0.62 μg/mL), followed by incubation at 37 °C for 24 h. Bacteria incubated with 1 mM of H2O2 were considered as a positive control, and as negative control cells without CuONPs were used.
After the treatment with CuONPs, cells were washed thrice with 200 μL of PBS 1× and incubated at 37°C in darkness with 100 μl of DCFDA (20,70-dichlorofluorescein diacetate, 45 μM) (D6883 Sigma-Aldrich) for 60 min. Fluorescence (λex = 485 nm and λem = 520 nm) was measured using a Cary Eclipse fluorescence spectrophotometer (Agilent Technologies CA, USA).
2.9. Ultrastructural analysis of bacteria
The interaction of CuONPs with bacteria was analyzed for Gram-negative
E. coli and Gram-positive
S. aureus. Strains were grown in MHB with CuONPs at the MIC obtained for each strain, also control cultures were prepared using the following protocol: After incubation for 24 h, cells were fixed with 2.5% glutaraldehyde in 0.05 M sodium phosphate for 30 min. at ambient temperature. Then, cells were post-fixed with 2% OsO
4 at 4 °C for 2 h. Subsequently, samples were dehydrated in ethanol series and then infiltrated in Spurr resin/ethanol according to [
38]. Samples were then polymerized at 60°C for 24 h, afterwards sections of 70 nm thick were obtained in a Leica Ultracut-R ultramicrotome (Leica Microsystems Inc., Buffalo Grove, IL, USA). Samples were mounted in formvar/carbon 75 mesh copper grids and analyzed under TEM (Hitachi H7500), operated at 100 keV. For better CuONPs detection, sections were not post-stained.
2.10. Effect of CuONPs in mammalian cell lines
The effect of CuONPs in cell lines was evaluated in the Madin-Darby canine kidney cell line (MDCK), a macrophage cell line (RAW 264.7) and a hepatocyte cell line (AML-12). To determine the susceptibility of the different cell lines to CuONPs, a 96-well microplate was used, each well containing 10,000 cells in a final volume of 100 µL. Cells were incubated at 37 °C with 5% CO2 for 24 h. After incubation, the culture medium was discarded and the cells were exposed to different volumes of CuONPs (22.2, 11.1, 5.55, 2.775, 1.385 and 0.687 µL), obtained with the aqueous extract and supernatant of G. sessile. DMEM culture medium without CuONPs was the positive control, and 1% Triton X-100 in PBS was the negative control. The final volume of the wells was adjusted to 100 µL with supplemented DMEM medium, and the plate was incubated at 37 °C with 5% CO2. After 24 h of incubation with CuONPs, the culture medium was discarded, and the cultures were washed three times with 200 µL of PBS. To determine cell viability, the colorimetric method of the reduction of (3-[4,5-dimethylthiazol-2-yl]-2,5 diphenyl tetrazolium bromide) (MTT) was used (Sigma Aldrich M-8910). The absorbance was read with a UV-vis spectrophotometer (Thermo Scientific Multiskan GO) at 570 nm and 690 nm. All MTT reduction assays were performed independently in triplicate.
2.11. Statistical analysis
Statistical analysis was performed using the GraphPad Prism 9.3.0 software. The average size of NPs was calculated measuring 1000 NPs of each sample. Plotted data were reported as mean ± standard deviation. Two-way ANOVA followed by a Tukey test was used to detect significant differences in the mammalian cell viability assays.
4. Discussion
The biological synthesis of metallic NPs is considered an efficient and less toxic method [
22,
42]. Multiple studies report silver and gold NPs for biomedical applications, and recently copper oxide, zinc oxide, and iron oxide NPs are being considered [
27,
28,
29,
30]. The use of CuONPs has increased exponentially; they are being used in various applications such as industrial catalyst, gas sensors, electronic materials, biomedicine and environmental remediation [
43]. Biosynthesized copper NPs have also been proposed for photocatalytic, antimicrobial, and optical sensor applications, among others [
44,
45,
46]. Also, biosynthesized copper NPs have been reported for potential medical applications because of their anticancer, antimicrobial, antioxidant, and antidiabetic properties [
9,
31,
32]. Furthermore, copper is an essential trace element for life processes like energy metabolism, reactive oxygen species detoxification, iron uptake, multiple enzymatic reactions and signaling in eukaryotic organisms [
47,
48]. Thus, copper is essential for life, but it is highly reactive and can cause cell damage, so cells have mechanisms for copper homeostasis and thus be able to maintain safe levels of this element [
49]. However, it is well known that several factors provoke the toxicity of oxide NPs such as size, shape, surface modification and concentration [
43].
Therefore, it is crucial to evaluate if biosynthesized copper NPs, using non-pathogenic fungi, can control pathogenic microorganisms and simultaneously have a low toxicity effect in mammalian cell lines. Previous studies have reported using fungi to biosynthesize copper nanoparticles (CuNPs). They were found to possess antimicrobial, antidiabetic, anticancer, and antioxidant properties [
31,
50,
51].
In this work, we used
G. sessile, which is considered as a non-photogenic fungus, in fact members of the
Ganoderma family are considered as medicinal [
52]. It is important to mention that the resulting biosynthesized nanomaterial is polydisperse in most cases; however, to obtain the desired size range and shape, the adjustment of the reaction conditions such as temperature, pH, time, and reaction mixture concentration is needed. The pH adjustment is crucial for the biosynthesis of CuNPs and CuONPs [
31,
51,
53,
54]. For example, Noor et al. [
31], reported the pH adjustment for the synthesis of CuNPs using the extract of the fungus
Aspergillus niger with CuSO₄. It was noted that when adjusting the pH to 5, 7 and 8, the synthesis of CuNPs was only achieved under a pH of 7. In the green synthesis of CuONPs using
Galphimia glauca leaves and flowers extract, the authors observed that the most favorable pH for the synthesis of CuONPs was 12. While at low pH they reported that the activity of the carboxyl groups, present in the extract of
G. glauca decreased in such a way that with a pH of 2 they obtained larger spherical CuONPs (50-60 nm) with a greater tendency to agglomeration [
54]. The need to adjust the pH may be due to the decreased activity of reducing biomolecules due to the acidity of the precursor salt and/or the extract during the synthesis process. In this work, the pH of the 5 mM CuSO
4.5H
2O solution was 3.72, while the pH of the mixture of the supernatant and extract of
G. sessile with CuSO
4.5H
2O, was 3.18 and 3.37, respectively (ratio 1: 3). Therefore, for the synthesis of CuONPs using the aqueous extract and the supernatant of
G. sessile, it was necessary to adjust the pH to 10.
The obtained CuONPs were analyzed using spectrophotometry in the UV-visible light range, and a maximum absorbance was found at 290.73 nm using the supernatant and 296.10 nm using the extract of
G. sessile, similar to the maximum absorbance peak at 290 nm reported using the
Camellia japonica leaf extract [
45].
Regarding the sizes of the CuONPs, it was found that those obtained by TEM differ considerably from the hydrodynamic diameters obtained with DLS, which may be due to the adhesion of components (molecules, proteins) present in the extracts used from G. sessile. In addition, this material serves as a capping agent, which maintains the stability of NPs, evidenced by the zeta potential values (-28.7 and 24.8 mV for CuONPs-S and CuONPs-E, respectively).
Obtained nanoparticles were quasi spherical in shape, HRTEM and SAED analysis revealed their polycrystalline nature. The diffractograms revealed the presence of three copper compounds and both types of nanoparticles seem to have a considerable amorphous component, especially NPs made with the extract (E), this is expected from the biomass residues from the intracellular components. The copper(II) oxide signals, in NPs from the supernatant (S) are clearly visible, in NPs from the extract (E) they are just resolved. The additional signals belong to copper nitrate and there are a couple of signals at low angles that seem to coincide with a complex of Cu with OH and NH3, where could be due to the interaction of Cu+2 with OH and amino groups of the extract.
The profile of the FTIR spectra in the region between 3500 and 3250 cm‒1 has the characteristic appearance of compounds with N–H, either ammonia or amines, this bond can be formed between Cu and protein residues. In fact, these results coincide with what was found in the DRX analysis.
The antibacterial activity of the CuONPs was determined through the bacterial growth inhibition assay, the MIC obtained was 16.5 µg/mL for all bacterial strains when using CuONPs-E. It is important to mention that both types of CuONPs were stable and maintained their antibacterial capacity for 2.5 years at ambient conditions. The concentrations needed for bacterial inhibition can be considered low, since higher concentrations of copper NPs for
E. coli inhibition were reported by [
55], the MIC obtained for different strains were in a range of 140 to 280 µg/mL for
E. coli, 140 µg/mL for
S. aureus and 20 µg/mL for
Bacillus subtilis. In that study, the authors found that the Gram-positive
B. subtilis strain MTCC 441 was more sensitive to the copper NPs, than silver NPs. Other studies report that CuNPs are not antibacterial at concentrations lower than 200 µg/mL with some Gram-negative bacteria, such as
E. coli and
Salmonella typhimurium [
32].
Lipopeptide stabilized Cu
2O NPs of small size (30 ± 2 nm diameter) were reported to have antimicrobial activity against both Gram-positive and Gram-negative bacteria with a MIC of 62.5 μg/mL. Although, the IC50 reported was also higher than those concentrations reported in this study, they found 21.21 μg/L and 18.65 μg/mL for
P. aeruginosa and
B. subtilis, respectively [
27].
Some of the proposed mechanisms of the antibacterial effect are through the interaction and disruption of the bacterial cell membrane, which allows the loss of cytoplasmic content [
56,
57]. In our study, although no evident specific accumulation of CuONPs was detected, in
E. coli and
S. aureus a slight accumulation in the cell wall and cytoplasmic membrane was found, this contrasts with the results of [
27]. They reported that the ultrastructure of
B. subtilis and
P. aeruginosa remarkably changed after exposure to cuprous oxide NPs. They found a high accumulation of NPs attached to the surface of
B. subtilis, displaying low density regions due to permeability of the cell wall and leakage of cytoplasmic content. However, bacteria were exposed to higher concentrations and different type of NPs, lipopeptide stabilized Cu
2ONPs with a higher average size (30 ± 2 nm) were used [
27].
CuNPs have been reported to cause multiple toxic effects in
E. coli cells, such as the generation of ROS, lipid peroxidation, protein oxidation and DNA degradation [
58]. In addition, the antibacterial activity of CuNPs evaluated in
E. coli and
Proteus vulgaris revealed a dose-dependent bactericidal action. Exposure to NPs provoked ROS generation, loss of membrane permeability and finally leakage of cytoplasmic components. Those effects were reported as the cause of CuNP-induced bacterial cell death [
57].
Concerning to the oxidative stress that nanometals could cause to bacteria, it is well documented that elevated ROS production occurs when bacteria is exposed to high concentrations of AgNPs and Cu/CuONPs [
57,
58,
59,
60,
61]. The same was true in our study, although we used relatively low concentrations of CuONPs, we detected elevated ROS production in all bacteria only at the highest concentration of CuONPs tested.
It is possible that the ROS overproduction at relatively low concentrations of CuONPs is associated with the material used to biosynthesize our NPs; this could be related to the ability of organic molecules (present in the supernatant/extract) to interact with cell membranes. We need to investigate the hydrophilicity/hydrophobicity interactions between molecules contained in the fungal extracts herein used, which could be crucial to overpassing the natural barriers in cells. Indeed, ions produced by metals can interact with some electrons in the molecules of cells membranes, but it is probably that a synergic effect is produced by using the organic molecules in the extract and supernatant of
G. sessile, that provide the NPs a surface corona that can interact with biological systems [
62,
63,
64].
Nanometal oxides such as ZnO and CuO NPs synthesized by a sol–gel combustion route, were reported as excellent antibacterial agents against both Gram-positive and Gram-negative bacteria. However, the authors stated the importance of identifying the key physicochemical properties of nanometal oxides that govern antibacterial capacity and also the cytotoxicity to mammalian cells [
65].
In this respect, cellular toxicity produced by metal oxide NPs is well documented [
12,
66,
67]. However, the specific mechanisms of this toxicity are not yet fully described. There are different theories of the toxic effect on animal cells, one of them is based on the production of reactive oxygen species (ROS) as one of the determining factors of cell death [
54]. In this way, in the biomedical area, metallic NPs can act as a therapeutic agent and consider this toxic property as an undesired effect. Nevertheless, this toxic effect could be useful to limit and control highly lethal cancers. However, in some of the biomedical applications of CuONPs, and other metallic NPs, it is necessary to focus on minimizing toxicity. In such cases, CuONPs can be embedded in materials for medical use, providing the antibacterial effect only on contact with the surface, but without generating toxicity in those who handle it [
68,
69]. To reduce toxicity, in this study we used fungal supernatant and extract of a non-pathogenic fungus, which proved to have no-toxic response in three mammalian cell lines (
Figure 9). Nevertheless, CuONPs-E were less toxic for mammalian cells lines with IC50 of 29.5 µg/mL for macrophages and kidney cells, and for hepatocytes the IC50 was 14.7 µg/mL, close to the MIC found for bacteria (16.5 µg/mL). Then, these concentrations of Cu could be considered safe for humans since the World Health Organization (WHO) reported a value of 2.0 mg/L as a regulation or guideline for copper in drinking water [
70]. Also, only at high concentrations of Cu, animal studies have shown liver injury and inflammatory responses to Cu administered above 4 mg/kg/day [
71].
It is important to identify the degree of toxicity that CuONPs can produce, regardless of the synthesis method to produce them. Determining the toxic concentrations of CuONPs will allow knowing the safe concentrations for future applications in the biomedical area. In this work, the CuONPs synthesized with the extract proved to be less toxic than the CuONPs synthesized with the supernatant of G. sessile, allowing the appropriate selection for future applications.