Next Article in Journal
A Comprehensive Study on Folate-Targeted Mesoporous Silica Nanoparticles Loaded with 5-Fluorouracil for the Enhanced Treatment of Gynecological Cancers
Previous Article in Journal
Reduction in Pathogenic Biofilms by the Photoactive Composite of Bacterial Cellulose and Nanochitosan Dots under Blue and Green Light
 
 
Search for Articles:
Title / Keyword
Author / Affiliation / Email
Journal
Article Type
 
 
Advanced Search
 
Section
Special Issue
Volume
Issue
Number
Page
 
Journals
JFB
Volume 15
Issue 3
10.3390/jfb15030073
jfb-logo
Submit to this Journal Review for this Journal Propose a Special Issue
► Article Menu

Article Menu

share Share announcement Help format_quote Cite question_answer Discuss in SciProfiles thumb_up
...
Endorse textsms
...
Comment
first_page
settings
Order Article Reprints
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Antibacterial and Antibiofouling Activities of Carbon Polymerized Dots/Polyurethane and C60/Polyurethane Composite Films

by
Zoran M. Marković
1,*,
Milica D. Budimir Filimonović
1,
Dušan D. Milivojević
1,
Janez Kovač
2 and
Biljana M. Todorović Marković
1,*
1
Vinča Institute of Nuclear Sciences, National Institute of the Republic of Serbia, University of Belgrade, Mike Alasa 12-14, 11001 Belgrade, Serbia
2
Jozef Stefan Institute, Department of Surface Engineering, Jamova 39, SI-1000 Ljubljana, Slovenia
*
Authors to whom correspondence should be addressed.
J. Funct. Biomater. 2024, 15(3), 73; https://doi.org/10.3390/jfb15030073
Submission received: 8 February 2024 / Revised: 11 March 2024 / Accepted: 14 March 2024 / Published: 17 March 2024
(This article belongs to the Special Issue Photodynamic Therapy of Cancer, Microbes and Viruses)
Browse Figures
Versions Notes

Abstract

:
The cost of treatment of antibiotic-resistant pathogens is on the level of tens of billions of dollars at the moment. It is of special interest to reduce or solve this problem using antimicrobial coatings, especially in hospitals or other healthcare facilities. The bacteria can transfer from medical staff or contaminated surfaces to patients. In this paper, we focused our attention on the antibacterial and antibiofouling activities of two types of photodynamic polyurethane composite films doped with carbon polymerized dots (CPDs) and fullerene C60. Detailed atomic force, electrostatic force and viscoelastic microscopy revealed topology, nanoelectrical and nanomechanical properties of used fillers and composites. A relationship between the electronic structure of the nanocarbon fillers and the antibacterial and antibiofouling activities of the composites was established. Thorough spectroscopic analysis of reactive oxygen species (ROS) generation was conducted for both composite films, and it was found that both of them were potent antibacterial agents against nosocomial bacteria (Klebsiela pneumoniae, Proteus mirabilis, Salmonela enterica, Enterococcus faecalis, Enterococcus epidermis and Pseudomonas aeruginosa). Antibiofouling testing of composite films indicated that the CPDs/PU composite films eradicated almost completely the biofilms of Pseudomonas aeruginosa and Staphylococcus aureus and about 50% of Escherichia coli biofilms.

1. Introduction

Bacterial colonization can occur on various surfaces in different public places (hospitals, healthcare facilities, universities, public transport) [1]. A lot of parameters such as shear forces, bacterial motility and electrostatic and hydrodynamic interactions between the surface and microbial cells can contribute to the attachment of pathogens to surfaces [2]. The time that pathogens spend on various surfaces depends on the type of pathogen and can range from a few hours to several days. Besides respiratory, fecal–oral and sexual transmission, pathogen transfer throughout surfaces has a key role in human pathogenic infections, including nosocomial infections [3]. Surfaces present in hospitals (medical equipment surfaces, environment surfaces surrounding patients and corporal surfaces of patients and healthcare workers) may serve both as a reservoir and a vehicle of pathogen transmission [4,5]. The most common surfaces near patients are bedrails and mechanical ventilation tubes for patients who develop ventilator-associated pneumonia [6]. The most common bacteria strains that contaminate hospital surfaces are Methicillin-resistant Staphylococcus aureus (MRSA), Pseudomonas aeroginosa, Acinetobacter baumannii, Escherichia coli and Salmonella spp. [7]. MRSA contamination of environmental surfaces (overbed tables, bedside rails and curtains) in hospital rooms can be transmitted from these surfaces to patients by the hands [8]. Furthermore, it can be found everywhere in hospitals because it is spread by people (patients, visitors or healthcare workers). Pseudomonas aeruginosa is a primary cause of ventilated-associated pneumonia in intensive care units [9]. This bacteria is one of the most resistant pathogens to antibiotics. Acinetobacter baumanii belongs to the group of pathogens that can adapt to the hospital environment and resist different cleaning and disinfecting agents [10]. The time that pathogens can spend on surfaces determines the risk of pathogen transmission from contaminated surfaces to patients, hospital staff or even visitors [11]. A few parameters affect the ability of pathogens present in hospitals and other healthcare facilities to colonize and survive on surfaces: relative humidity, temperature, ability to form biofilm and the properties of surfaces themselves: wettability, surface roughness and porosity [12].
A biofilm is a microbe assembly enclosed in an extracellular polymeric matrix attached to various surfaces in different environments. A polymeric substance matrix is made up of proteins, polysaccharides or extracellular DNA [13]. The first phase in biofilm formation is the attachment of bacteria to the surface. Further, bacteria proliferate throughout the surface, and at the end, the bacterial community becomes mature. When the biofilm is formed, bacteria that are not resistant to various antibacterial agents can become resistant. This problem of bacterial resistance in applied medicines, i.e., antibiotics, has become more pronounced throughout the years. Due to its big impact on public health, comprehensive research needs to be conducted to understand how to prevent or reduce biofilm formation (which strategy needs to be applied to overcome problems related to biofilm formation).
Up to now, there are a few strategies that can be divided into three groups: (a) changing the properties of susceptible surfaces to prevent biofilm formation, (b) regulating signaling pathways to inhibit biofilm formation and (c) applying external forces to eradicate the biofilm [14]. For example, by using thermal cycling or UV irradiation, surface of potential antibiofilm materials can be treated; various coatings can be deposited on substrates (i.e., trimethylsilane (TMS)/O2 and antimicrobial peptides); by using chemical agents that influence quorum sensing, c-di-GMP-, c-di-AMP- and (p)ppGpp-related pathways; to eradicate mature biofilms, external forces (i.e., ultrasound) can be used [14].
Photodynamic antimicrobial therapy eradicates pathogens using commercial visible light sources and polymer composites that generate reactive oxygen species [15,16]. It is perfectly safe for medical staff and patients, and there are no toxic compounds that leach from composites and pollute the environment.
In our previous research, we encapsulated carbon quantum dots (CQDs) into polyurethane films and found that these composites eradicated Stafilococcus aureus (S. aureus) and Escherichia coli (E. coli) very efficiently for 1 h [17]. Later, we encapsulated carbon polymerized dots (CPDs) into polyurethane films and established their strong antibacterial potential, especially E. coli, for 1 h [18]. Other authors encapsulated metal nanoparticles (Cu, Au) into polyurethane films and described their antibacterial activity against S. aureus and E. coli [19,20,21,22]. Many bactericidal applications of carbon dot composites rely on combining the photodynamic reactive oxygen species production of carbon dots with the antibiotic activity of a transition-metal-based nanoparticle, often containing Ag, Cu, Zn or Ti oxides cores, among others [23]. Fullerenes can inhibit bacterial growth and metabolism. It was established that Gram-positive bacteria are more sensitive to fullerenes due to their higher membrane permeation [24]. The antibacterial activity of fullerenes is based on the electrostatic interaction between fullerenes and bacterial membranes or due to the reactive oxygen generation of fullerenes [25].
In this paper, we investigated the structural, chemical, antibacterial, antibiofouling and cytotoxic activities of CPD/polyurethane (CPD/PU) composite films and C60/PU composite films. We conducted electrostatic force microscopy (EFM) of composites, which is an electrical mode in atomic force microscopy (AFM) to monitor the variation in samples’ electric fields to obtain information on the charge content and distribution of nanocarbon fillers. We tested both composite film samples on seven different bacterial strains, including Klebsiela pneumoniae, Proteus mirabilis, Salmonela enterica, Enterococcus faecalis, Enterococcus epidermis, Shigella flexneri, Pseudomonas aeruginosa and fungi Aspergilus niger. Apart from antibacterial activity, we conducted antibiofouling tests against the following bacteria: Pseudomonas aeruginosa, Staphylococcus aureus and Escherichia coli.

2. Materials and Methods

2.1. Materials

Riboflavin (Carl Roth 97%, Karlsruhe, Germany), ethylenediamine (Carl Roth 99.5%, Karlsruhe, Germany), acetone (Honeywell p.a., Charlotte, NC, USA), toluene (Sigma Aldrich, Rahway, NJ, USA), fullerene C60 (Sigma Aldrich, Rahway, NJ, USA), a nylon membrane filter of 100 nm pore size (Tisch Scientific, Cleves, OH, USA), Sensor Green (Invitrogen, Thermo Fischer Scientific, Waltham, MA, USA), D-Chloroform (Sigma Aldrich, Rahway, NJ, USA) were purchased and used as received. Super clear medical grade high stretch polyurethane waterproof transparent TPU film was purchased by DG Xionglin New Materials Technology, Dongguan, China. The thickness of the film was 0.2 mm.

2.2. Sample Synthesis

Carbon polymerized dots (CPDs) were synthesized by solvothermal procedure from riboflavin and ethylenediamine mixed in acetone, as described previously [18]. The CPD/PU composite films were synthesized by the following procedure: polyurethane pieces (50 × 50 × 0.2 mm3) were inserted in CPD solution in acetone (50 mL). The CPD concentration was 145 mg/mL. To encapsulate CPDs in polyurethane, swelling–shrink encapsulation method was applied [17]. The swelling time was 1 h at room temperature. After that, CPD/PU composite films were dried in vacuum furnace at 80 °C for 12 h.
C60 was dissolved in toluene with concentration of 1 g/L. The C60/PU composite films were prepared by using the same method as the CPD/PU composite films. The swelling time was 24 h at room temperature.

2.3. Sample Characterization

To visualize the surface of CPD nanoparticles, CPD/PU and C60/PU composite film AFM was used with AC160 cantilever (MFP-3D Origin, Asylum Research, Oxford Instruments, Santa Barbara, CA, USA). The microscope was operated in tapping and viscoelastic mode at room temperature. Nanoparticle size (diameter and height), typical structure of CPDs and Young’s modulus were calculated from more than 10 AFM images in Gwyddion software (Gwyddion 2.64) [26]. To determine Young’s modulus, microscope was operated in AM-FM Viscoelastic mapping mode (AC 160 cantilever, which operated at 320 kHz and 2 MHz) [27]. Distribution of Young’s modulus was determined from frequency, amplitude and phase of the two modes with a contact mechanics model.
Electrostatic force microscopy (EFM) measurements were performed at room temperature with an MFP 3D Origin (Asylum Research, Oxford Instruments, Santa Barbara, CA, USA). A Si cantilever coated with Ti-Ir (ASYELEC-01) was used. A cantilever resonant frequency v0 of 75 KHz, Q factor of 130 and a spring constant k of 2.8 N/m were measured using a thermal noise method. Tip voltage 3 V was typically used. All EFM data were collected from the surface of CPD nanoparticles deposited on freshly cleaved mica by spin coating method and CPD/PU and C60/PU composite films. Polymer composite film samples were cleaned with 96% ethanol before each measurement. The distribution of CPDs and C60 in the PU was studied by EFM (phase mode).
To determine chemical composition of CPD and fullerene C60 film samples, X-ray photoelectron spectroscopy (XPS) analysis of the surface of the CPDs and C60 film was carried out on the PHI-TFA XPS spectrometer produced by Physical Electronics Inc. and equipped with Al-monochromatic source and hemispherical electron energy analyzer. The analyzed area was 0.4 mm in diameter, and the analysis depth was 3–5 nm. Pass energy during the XPS analyses was 29 eV, resulting in an energy resolution of 0.65 eV. Two places were analyzed, and XPS spectra were very reproducible. The C 1 s spectrum was aligned to binding energy of 284.5 eV, characteristic of C-C/C-H bonds. The accuracy in the binding energy of XPS spectra was ±0.3 eV. Quantification of surface composition was performed from XPS peak intensities, taking into account relative sensitivity factors provided by instrument manufacturer [28]. XPS data were processed by the Multipak program ver. 9.9.
Fourier-transform infrared spectroscopy (FTIR) measurements of all samples were performed on a Nicolet iN10 Thermo Fischer Scientific operated in ATR mode. Both C60 and CPD samples were deposited on Si substrates using drop-casting method. Spectral resolution was 4 cm−1, whereas the spectra were recorded in the range of 400 to 4000 cm−1 at room temperature.
UV-Vis spectra of the CPDs, C60 toluene solution, CPDs/PU and C60/PU composite films were recorded on a Unispec2 LLG spectrophotometer in air at room temperature. The measurement range was from 200 to 700 nm.

2.4. Production of Reactive Oxygen Species

To measure singlet oxygen production of composite film samples, we used two methods: measurement of photoluminescence (PL) at 530 nm of sensor green singlet oxygen (SOSG) as fluorescence probe and measurement of decay of absorption spectra of 9,10-Anthracenediyl-bis(methylene)dimalonic acid (ABDA) at 400 nm.
The first method represents the measurement of PL of SOSG, which was used as fluorescence probe. The concentration of SOSG in methanol solution was 12 µmol. The sample (8 × 8 mm2) was dipped in methanol solution of SOSG. Both samples, CPDs/PU and C60/PU composite films, were irradiated by blue lamp (3 W, V-TAC, Bulgaria) at wavelength of 470 nm. The sample irradiation time ranged from 1 to 11 min, and after irradiation, immediately, the measurements were conducted on Fluoromax + 4 spectrofluorometer (Horiba, Kyoto, Japan). The PL spectra were measured under 488 nm excitation in the range of 500–800 nm [29]. The measurement step was 1 nm.
The second method was based on the measurement of the absorption spectra of 9,10-Anthracenediyl-bis(methylene)dimalonic acid. ABDA (Merck, Burlington, MA, USA) was used as received. A stock solution of ABDA in ethanol (Sigma Aldrich, Sigma Aldrich, Rahway, NJ, USA) of ~10 mM was used. The solution was diluted till absorbance measurement showed that the absorbance at 400 nm was 1 [30]. For irradiation experiments, the solutions were placed into a 10 mm path length cuvette. Then, CPD/PU and C60/PU samples (8 × 8 mm2) were placed at the bottom of cuvette. Both samples were irradiated by blue light at 470 nm, 3 W. At regular intervals (60, 120 and 180 min), irradiation was stopped, and the absorbance spectra were recorded on an LLG-UNISPEC2 spectrophotometer (LLG, Meckenheim, Germany). All irradiation experiments were repeated three times.
To measure hydroxyl radical production, the following procedure was applied: The samples (CPD/PU and C60/PU composite films, 8 × 8 mm2) were immersed in 3 mL of terephthalic acid (TA, Sigma Aldrich), water/NaOH (2 × 10−3 mol/L) solution. The TA concentration was 5 × 10−4 mol/L. Both samples were irradiated with blue lamp at 470 nm in intervals of 0–90 min [31]. The luminescence of the formed hydroxyterephthalic acid (h-TA) solutions was measured on Fluoromax + 4 spectrofluorimeter (Horiba, Kyoto, Japan) under excitation wavelength of 330 nm.

2.5. Antibacterial Activity

Antibacterial activity of CPD/PU and C60/PU composite films was tested according to International Standard ISO 22196 (Plastics—Measurement of antibacterial activity on plastic surfaces) [32]. Following species of bacteria were used: Klebsiela pneumoniae ATCC13883 (K. pneumonie), Proteus mirabilis ATCC 14153 (P. mirabilis), Salmonela enterica ATCC 13076 (S. enterica), Enterococcus faecalis ATCC29212 (E. faecalis), Enterococcus epidermis ATCC 12228 (E. epidermis), Shigella flexneri ATCC 12022 (S. flexneri), Pseudomonas aeruginosa ATCC 27853 (P. aeruginosa), Aspergilus niger ATCC 16404 (A. niger).
All tests were performed in triplicate, and adequate controls for untreated samples were used (three to measure viable cells immediately and three to measure viable cells after incubation for 24 h). All tested materials—CPD/PU and C60/PU composite films—were prepared as flat squares, 50 mm × 50 mm, sterilized by UV lamp at 258 nm for 30 min. Untreated specimens were used for control of bacterial viability, and other material specimens were incubated under blue light at 470 nm for 1 h. Specimens were inoculated with 0.4 mL bacterial suspension of 2.9–15.2 × 107 cell/mL. Test inoculums were covered with films (40 mm × 40 mm), and Petri dishes with test specimens were incubated for 24 h at 35 °C, humidity 90%. Bacteria were recovered with 10 mL of SCDLP, and 10 µL (different dilutions) were plated on LB agar and incubated for 24 h at 35 °C, after which bacterial colonies were counted. The distance from the blue lamp and samples was 50 cm to provide homogeneous irradiation of the samples.
N—number of viable bacteria recovered for test specimen
N = (100 × C × D × V)/A
C—average plate count, D—dilution factor for the plate counted, V—volume (mL) of SCDLP added, A—surface area (mm2) of the cover film.
R—antibacterial activity of tested material
R = (Ut − U0) − (At − U0) = Ut − At
U0—average of log 10 of the number of bacteria from nonirradiated sample in 0 h, Ut—average log 10 of the number of bacteria from nonirradiated sample after 24 h, At—average log 10 of the irradiated sample after 24 h.

2.6. Antibiofilm Activity Testing

For testing antibiofilm effect of composite films, strains of the following bacteria were used: Staphylococcus aureus NCTC 6571, Pseudomonas aeruginosa ATCC 10332 and Escherichia coli NCTC 9001. All materials tested were gently wiped with 70% ethanol, dried and exposed to blue light for 1 h (except untreated control). Using sterile forceps, the materials were then placed in the wells of 6-well microtiter plates. Overnight cultures of different bacteria were diluted 1000-fold (1–5 × 108 cell/mL) and added to 5 mL of fresh, sterile LB medium. Fresh LB medium was added to each well, with a total volume of 5 mL covering the materials. In the test wells, 5 µL of overnight culture was added, while 5 µL of fresh LB medium was added to the control wells. The plate was incubated for 24 h at 37 °C with a rotation rate of 110 RPM.
After incubation, the LB medium was removed, and the materials were washed twice with dH2O and dried for 20 min. A 0.1% crystal violet solution was added to each well in a total volume of 3 mL, and the materials were incubated with the stain for 20 min. Following this, the materials were washed twice with dH2O and dried. After 20 min, a solution of 30% acetic acid was added to each well in a total volume of 3 mL. Absorbance was measured at 550 nm after 100 µL of acetic acid from each well was transferred to wells of a 96-well microtiter plate. All materials with bacteria were incubated in triplicate, and all controls were incubated in duplicate.

2.7. Cytotoxicity

To assess cytotoxicity (antiproliferative activity), standard MTT assays were used, and methods were suitable for materials testing (ISO Standard 10993-5) [33,34]. All tests were performed in triplicate. Human epidermal keratinocyte line (HaCaT) cell line (T0020001) was commercially obtained from AddexBio Technologies (San Diego, CA, USA). These are in vitro spontaneously transformed keratinocytes from histologically normal skin. The HaCaT cells plated in a 96-well flat-bottom plate at a concentration of 1 × 104 cells/well, grown in humidified atmosphere of 95% air and 5% CO2 at 37 °C, and maintained as monolayer cultures in RPMI-1640 medium supplemented with 100 µg/mL streptomycin, 100 U/mL penicillin and 10% (v/v) fetal bovine serum (FBS). Material samples were ethanol washed. Sample extracts were prepared by incubating material samples (1 mg/mL) in RPMI-1640 medium for 72 h at 37 °C. RPMI-1640 medium, in which HaCaT cells were maintained as monolayer cultures, was replaced with undiluted sample extract (100%), 50%, 25% and 12.5% sample extracts (prepared by diluting sample extracts with fresh RPMI-1640). After 48 h of treatment with sample extracts, cell proliferation was determined using MTT reduction assay by measuring absorbance at 540 nm and 670 nm on Tecan Infinite 200 Pro multiplate reader (Tecan Group, Männedorf, Switzerland). The results are presented as a percentage of the control (untreated cells), which was arbitrarily set to 100%.

3. Results

3.1. Surface Morphology of CPD, CPDs/PU and C60/PU Composite Films

The surface morphology of CPD, CPDs/PU and C60/PU composite films was investigated by AFM operating in tapping mode. Figure 1a,b show the surface morphology of the CPD nanoparticles recorded in height and phase modes. It was observed that the CPD nanoparticles had a core–shell structure with a typical average core diameter of 33 nm (Figure 1b, phase retrace mode). In our previous research, we established that the average core diameter of CPDs was 35.2 ± 2.1 nm [18]. The average diameter of the whole nanoparticle (core–shell) was 60 nm, whereas the average height was 3 nm.
Viscoelastic measurement of Young’s modulus of the CPDs is presented in Figure 1c,d. It was confirmed that the core–shell structure of the CPDs was revealed by phase measurement. Figure 1d presents Young’s modulus profile of the CPD nanoparticles, designated with a black line in Figure 1c. From Figure 1d, we can see that Young’s modulus of the shell and core was about 16 and 10 Gpa using the Hertz model, respectively.
Figure 2 shows the surface morphology of neat polyurethane (PU), CPD/PU and C60/PU composite films. By Gwyddion software, we calculated the root mean square (RMS) roughness of these polymer composite films. The values of RMS roughness were the following: 3.14 nm (neat PU), 8.60 nm (CPDs/PU) and 8.39 nm (C60/PU). Encapsulation of CPDs and C60 into the polymer matrix increased RMS roughness by 2.74 and 2.67 times, respectively.

3.2. Electrostatic Force Microscopy of CPDs, CPDs/PU and C60/PU

Electrostatic force microscopy (EFM) is a very useful method for detecting the charge of a single nanoparticle or nanoparticles dispersed in an insulating polymer matrix or on an insulating surface. This technique enables imaging of the distribution and uniformity of charged carbon-based nanoparticles inside polymers. EFM images can be quantitatively related to charge distributions on a sample surface through mathematical modeling of the tip–sample interaction [35]. Several authors studied the distribution of conductive carbon nanotubes and graphene in a polymer matrix and developed theoretical models that describe the architecture of a polymer composite [36,37,38,39].
All EFM data were collected from the surface of CPD nanoparticles deposited on freshly cleaved mica by the spin coating method and the surface of CPD/PU and C60/PU composite films. Figure 3a,d,g show the top view of AFM images (left column) of CPD nanoparticles and CPD/PU and C60/PU composite films, respectively. Figure 3b,e,h present the EFM phase images (right column) of CPD nanoparticles and CPD/PU and C60/PU composite films, respectively. Data in Figure 3b indicate the presence of negatively charged carriers—electrons in the core of CPDs (negative phase of electrical signal compared with phase on the surface of mica). The presence of electrons in the CPD core helped us to detect CPD nanoparticles inside the polymer matrix (black voids) in Figure 3e. Similar data with smaller intensities were obtained after EFM microscopy of the C60/PU composite film. This result indicates that CPD and C60 clusters are located in the pores of polyurethane polymer. The intensity of the electrical phase signal was considerably stronger for CPDs/PU than for C60/PU, which corresponds to the expected charge distribution. Figure 3c,f,i show the charge distribution profile of CPD nanoparticles, the charge distribution profile of CPD nanoparticles encapsulated in the interior of CPDs/PU and the charge distribution profile of C60 clusters in the PU polymer film, respectively. The CPDs have much more electrons (phase in the range of 1–4.5 degrees), see Figure 3e, than the cluster of C60 molecules (range 0.3–0.8 degrees), as shown in Figure 3h, located in a nearly identical polyurethane pore.

3.3. Chemical Composition

The XPS technique was used to determine the chemical composition of the CPD nanoparticles (elemental composition and characteristic bonds identified) and fullerene C60 film. The data presented in Table 1 indicate that the content of C was the highest (83.1 At%), whereas the content of oxygen was the lowest (7.3 At%) for the CPD sample. Table 2 presents the characteristic bonds identified in the CPDs sample and the relative concentration of these bonds in % with respect to the total amount of the specific element (C, O, N). The content of pyrrolic bonds was the highest. C=N-C bonds were also detected, and the presence of these bonds contributed to the new properties of these dots.
Table 1 lists the content of the C60 film as well. From this table, we can observe that the content of C 1 s was the highest (90 At%), whereas the content of O 1 s was 10 At% for the C60 film sample.
Table 2 lists the binding energies of the characteristic bonds identified in the C60 film and the relative concentration of these bonds in % with respect to the total amount of the specific element (C, O). It is known that O2 or H2O molecules are physisorbed on C60 molecules, and the presence of an O 1 s peak in the XPS spectrum of C60 originates from that [40].
Figure S1a presents the FTIR spectra of C60 (green curve) and the CPD nanoparticles (red curve). The following spectra were identified in the FTIR spectra of the CPD nanoparticles: the peak at 3300 cm−1 could be assigned to O-H stretching vibrations in the intermolecular bonding, whereas the peaks at 2956 and 2871 cm−1 originated from C-H stretching vibrations of the CH3 groups. The peak at 2922 cm−1 stemmed from C-H stretching vibrations of the CH2 groups. At 1666 cm−1, we identified C=N stretching vibrations, whereas at 1435 cm−1, we detected O-H bending vibrations. The peak at 1367 cm−1 stemmed from N-O symmetric stretching vibrations, whereas the peak at 1290 cm−1 was assigned to a C-N stretching aromatic amine. The peak at 881 cm−1 originated from C-H bending vibrations [41].
The following peaks were detected in the FTIR spectra of the C60 toluene solution: the peak at 3462 cm−1 stemmed from O-H stretching vibrations in the intermolecular bonding, the peaks at 2956 and 2860 cm−1 were assigned to C-H stretching vibrations of the CH3 groups and the peak at 2930 cm−1 originated from C-H stretching vibrations of CH2 groups. The peak at 1624 cm−1 stemmed from C=C stretching vibrations, whereas the peak at 1454 cm−1 was assigned to C-H bending vibrations. The peaks at 1256 and 1043 cm−1 originated from C-O stretching vibrations. The obtained spectra agree with the recorded XPS spectra.
Figure S1b shows the FTIR spectra of neat PU (black curve), CPDs/PU (red curve) and C60/PU (green curve). The following peaks were identified in the spectrum of neat PU: the peak at 3335 cm−1 was due to O-H stretching vibrations, the peaks at 2962 and 2866 cm−1 stemmed from stretching vibrations of the CH3 groups; the peaks at 1738 and 1701 cm−1 were assigned to C=O bonds; the peak at 1594 cm−1 was due to C=C bonds; the peak at 1525 cm−1 originated from N-O stretching vibrations; the peaks at 1414 and 1313 cm−1 corresponded to O-H bending vibrations; the peaks at 1228, 1169 and 1073 cm−1 were assigned to C-O stretching vibrations; the peaks at 818 and 770 cm−1 stemmed from C-H bending vibrations.
In the case of CPD/PU composite films (red curve), we identified the following peaks: the peak at 3206 cm−1 was due to O-H stretching vibrations; the peaks at 2956, 2919 and 2850 cm−1 stemmed from C-H stretching vibrations; the peaks at 1734 and 1695 cm−1 were assigned to C=O bonds, whereas the peak at 1598 cm−1 was due to C=C bonds; the peak at 1636 cm−1 originated from C=N stretching vibrations and was down-shifted by 30 cm−1 compared with the same peak of CPDs nanoparticles; the peak at 1524 cm−1 originated from N-O stretching vibrations; the peaks at 1412 and 1313 cm−1 were due to O-H bending vibrations; the peak at 1369 cm−1 stemmed from N-O symmetric stretching vibrations, and there was an up-shift by 2 cm−1 compared with the same peak of CPD nanoparticles; the peaks at 1225, 1108 and 1073 cm−1 were assigned to C-O; the peaks at 818 and 770 cm−1 could be detected as C-H bending vibrations. The peak at 1290 cm−1 identified in the FTIR spectrum of CPD nanoparticles could not be detected in the polymer composite film sample.
The FTIR spectrum of C60/PU composite films (green curve) showed the following peaks: the peak at 3302 cm−1 was due to O-H stretching vibrations; the peaks at 2919 and 2850 cm−1 stemmed from C-H stretching vibrations, whereas the peaks at 1732 and 1698 cm−1 were due to C=O bonds; the peak at 1634 cm−1 originated from C=C vibrations and was up-shifted by 10 cm−1 compared with the same peak of C60; the peak at 1525 cm−1 originated from N-O stretching vibrations; the peaks at 1412, 1371 and 1312 cm−1 originated from O-H bending vibrations; the peaks at 1222, 1105 and 1068 cm−1 were due to C-O bonds, whereas the peaks at 813 and 770 cm−1 stemmed from C-H bending vibrations.
Table S1 lists the position of the characteristic bonds and shifts (∆) identified in all samples in cm−1. From this table, we can observe the position shifts of the characteristic peaks in both composite film samples. The obtained results indicate the encapsulation of certain fillers into the polymer matrix.

3.4. UV-Vis Spectra of CPD and C60 Nanoparticles

The UV-Vis absorbance spectra of CPD nanoparticles and C60 toluene solution are presented in Figure S2a. Both absorbance spectra were normalized to 1. From this figure, we can observe two peaks only: for the CPD (red curve) acetone solution, we detected peaks at 258 and 330 nm, respectively. The first peak was assigned to the π-π* transition of C=C bonds. The other peak belongs to the n-π* transition of C=O bonds [42]. A similar UV-Vis absorbance spectrum was recorded for the C60 toluene solution. Two peaks were identified in the absorption spectrum of C60: a peak at 254 nm, which corresponded to C=C due to the π-π* transition, and another peak at 330 nm.
The UV-Vis absorption spectrum of the CPD/PU composite films (red curve) consisted of a peak at 350 nm and a wide shoulder at 380 nm (Figure S2b). The first peak corresponded to a n–π* transition of C=O, whereas the peak at 380 nm was assigned to C=N-C bonds due to the presence of graphitic nitrogen [43,44]. The absorption spectrum of the C60/PU composite films (black curve) shows the presence of only one peak at 392 nm.

3.5. Production of Reactive Oxygen Species

3.5.1. Production of Singlet Oxygen

In our previous research, we established that different types of carbon dots (carbon quantum dots (CQDs), graphene quantum dots (GQDs) and doped carbon quantum dots (DCQDs)) produced reactive oxygen species under blue light irradiation [45]. Recently, we found for the first time that CPDs produced singlet oxygen and superoxide anions under blue light irradiation at 470 nm [18]. Until now, there have been two proposed mechanisms of ROS production: Ge et al. claimed that GQDs produce singlet oxygen through energy transfer to molecular oxygen [46], whereas Chong et al. found that besides singlet oxygen, superoxide anion could be involved in the production of ROS [47]. Thus, electron transfer is an intermediate step for the generation of singlet oxygen of GQDs under blue light irradiation.
Figure 4 shows the production of singlet oxygen of CPD/PU (Figure 4a) and C60/PU (Figure 4b) composite films and the production rate of singlet oxygens of CPD/PU and C60/PU samples (Figure 4c). Figure 1a shows that the intensity of the absorption peak of SOSG at 533 nm increased with blue light irradiation time. A similar phenomenon occurred for C60/PU samples (Figure 4b). But from Figure 4c, we can observe that the production rate of singlet oxygen is higher for the CPD/PU samples.
Figure 4d,e represent the decay of the absorption peak of ABDA molecules in the presence of blue-light-irradiated CPD/PU and C60/PU samples. From this figure, we can observe the photobleaching of ABDA for different time intervals (60, 120 and 180 min), respectively. As can be seen from Figure 4d,e, the photobleaching of ABDA is much higher for the CPDs/PU samples. In the case of the CPD/PU sample, the decolorization of ABDA was complete after 180 min of blue light irradiation. At the same time, the ABDA decolorization, i.e., the ABDA absorbance intensity, decreased in the presence of C60/PU composite films by only 15% after 180 min of blue light irradiation.

3.5.2. Production of OH Radicals

It is very important in antibacterial photodynamic treatment to find out if the tested polymer composite films generate other types of ROS. To establish whether these composite films produce hydroxyl radicals, we conducted the measurements using a solution of terephthalic acid as a fluorescent probe. From Figure 5a, we can conclude that there was OH radical production in the CPD/PU samples, whereas there was no hydroxyl radical production in the C60/PU samples; see Figure 5b.

3.6. Antibacterial Activity of CPD/PU and C60/PU Polymer Composite Films

The antibacterial activity of CPD/PU and C60/PU composite films was investigated against seven bacteria strains (K. pneumonie, P. mirabilis, S. enterica, E. faecalis, S. epidermis, S. flexneri, P. aeruginosa) and fungi (A. niger). Table 3 presents the results of the antibacterial activity of these composites with and without blue light irradiation for 1 h. The results in Table 3 show that the most sensitive bacteria on CPDs/PU were K. pneumonie, P. mirabilis, S. enterica, E. faecalis, E. epidermis and P. aeruginosa under blue light irradiation for 1 h.
The results in Table 3 show that all tested bacteria and fungi were sensitive on the C60/PU composite films under blue light irradiation for 1 h. Some bacteria strains are sensitive on the C60/PU composite films in the absence of blue light irradiation: K. pneumonie, P. mirabilis, S. enterica, E. faecalis and P. aeruginosa. Fungi A. niger was sensitive on the C60/PU composite films in both conditions: with or without blue light irradiation.
The results presented in Table 3 indicate that both types of tested polymer composites are potent antibacterial agents. Under blue light irradiation, the C60/PU composite films eradicated Shigella flexneri completely, whereas the CPD composite films eradicated 75% of these bacteria strains. K. pneumonie and S. epidermis were sensitive on the CPD/PU composite films both with and without blue light irradiation. The C60/PU composite films acted very strongly on K. pneumonie, P. mirabilis, S. enterica and P. aeruginosa, both with and without blue light irradiation.
The mechanism of their antibacterial activity is the following: both samples generated reactive oxygen species based on the data presented in Figure 4 and Figure 5. The CPD/PU composite films produced singlet oxygen and hydroxyl radicals, whereas C60/PU generated only singlet oxygen under blue light irradiation. The produced ROS induced bacterial membrane damage and further oxidative stress [48]. Compared with the results presented in Table 3, we can conclude that C60/PU composite films were more toxic on a wide range of tested bacteria.

3.7. Antibiofouling Activity of CPDs/PU and C60/PU

It is very important to observe the formation, reduction or even eradication of biofilms of different bacteria strains. In this research, it was very interesting to observe the antibiofouling activity of the CPD/PU and C60/PU composite films against bacteria strains present in hospitals: P. aeruginosa, S. aureus and E. coli. Figure 6a–c shows the antibiofouling activity of both types of testing composite films against three bacteria: P. aeruginosa, S. aureus and E. coli.
The results indicated the following: biofilm formation on both the CPDs/PU and C60/PU composite films was strain dependent, and differences were observed between blue-light-irradiated and nonirradiated samples. Under blue light irradiation, P. aeruginosa biofilm was reduced by 97% on the CPD/PU composite films and by only 20% on the C60/PU composite films; see Figure 6a. The CPD/PU composite films had potent antibiofouling activity against P. aeruginosa with blue light irradiation. Under the same conditions, S. aureus biofilm was reduced by 95% on the CPD/PU composite film and by 65% on the C60/PU composite film; see Figure 6b. These composite films showed antibiofilm activity against this bacterium without blue light irradiation: 94% of bacteria biofilm was reduced on the CPD/PU composite films and 75% of bacteria biofilm on the C60/PU composite films, respectively. In the case of E. coli, CPDs/PU composite films reduced 50% of the bacteria biofilm, whereas the C60/PU composite films reduced 45% of the bacteria biofilm under blue light irradiation; see Figure 6c. Both composite films showed better antibiofouling activity against S. aureus and E. coli under blue light at 470 nm.

3.8. Cytotoxicity

To investigate the cytotoxicity of our samples, we tested them on human keratinocyte cell lines (HaCaT). The skin is an organ that is continually self-renewing and participates actively in host defenses [49]. Epidermal cells consist mostly of keratinocytes (about 95%). These cells have an important role as a barrier layer of the epidermis as well as in the initiation and perpetuation of skin inflammatory and immunological responses [50].
But fresh keratinocytes require supplementary growth factors to survive and proliferate in vitro, and once induced to differentiate, they rapidly die and do not allow long-term investigation of differentiation signals [51].
To minimize these problems, the spontaneously immortalized human keratinocyte cell line HaCaT from adult skin has been proposed as a model for the study of keratinocyte functions. HaCaT is a nontumorigenic monoclonal cell line adapted to long-term growth without feed-layer or supplemented growth factors [51]. Figure 7 shows the viability of HaCaT cells after being treated with neat PU as the control sample and the CPD/PU and C60/PU composite film samples.
The control sample did not show any toxicity under any concentration and without blue light irradiation. The CPD/PU composite film sample did not show any toxicity at concentrations of 12.5, 25 or 50% and showed severe toxicity at a concentration of 100%. Similar results were obtained for C60/PU composite film samples. The C60/PU composite film sample did not show any toxicity at concentrations of 12.5 or 25%, whereas they showed mild toxicity at a concentration of 50% and severe toxicity at a concentration of 100%. All experiments were performed in the dark without irradiation.

4. Discussion

In this research, we investigated the antibacterial and antibiofouling activities of CPD/PU and C60/PU composite films. Apart from these properties, we investigated their structural, chemical, electrical and optical properties. Structural analysis of nanoparticles encapsulated into polymer films conducted by AFM showed that the CPD nanoparticles had a core–shell structure and an average diameter of 33 nm. Electrostatic force microscopy enabled the determination of the charge type, content and distribution of the CPD nanoparticles and C60 clusters and showed that both filler particles were located in the interior of the polymer matrix. It was found that CPDs have much more electrons than the cluster of C60 molecules located in the nearly identical polyurethane pore. Before antibacterial and antibiofouling testing, we performed the measurements of ROS production by two methods: (1) by using SOSG as a fluorescence probe and measuring its PL at 530 nm and (2) by using ABDA color and measuring decolorization vs. time. It was established that CPDs/PU and C60/PU generated singlet oxygen. Furthermore, it was found later that CPD/PU composite films also produced hydroxyl radicals. None of these composite films showed cytotoxicity against HaCaT cell lines at concentrations ranging from 12.5 to 50%. Antibacterial testing showed that both composite films had strong antibacterial activity against investigated bacteria strains under blue light irradiation for 1 h.
The obtained results indicated that the CPD/PU composite films produced both singlet oxygen and hydroxyl radicals under blue light irradiation at 470 nm. The mechanism of ROS generation is related to negative charge transfer from photosensitizers (CPDs) to oxygen molecules. CPDs are produced from riboflavin and carbon molecules with abundant nitrogen atoms. During the carbonization process in a hydrothermal reactor, nitrogen-doped CPDs are produced. Nitrogen is a rich source of electrons that transfer charge to carbon, which is detected by EFM in the form of an electron cloud over a CPD surface. Similar to an atom, the greatest density of electrons is in the center of CPDs. Since polyurethane is a polymer with the highest oxygen diffusion rate among polymers, oxygens easily collide with CPDs, transferring to one of two detected ROS species and diffusing to the polymer surface [52].
On the other hand, during blue light irradiation of the C60/PU samples, only singlet oxygen was generated. Since the C60 cluster charge was much smaller than for CPDs, the dominant way for singlet oxygen generation is energy transfer from C60 molecules encapsulated in the interior of polymer films to molecular oxygen. C60 is composed of pure carbon, and there is no dopant to donate extra electrons. Thus, we prepared two types of composite films with different mechanisms of ROS generation, and it would be interesting to monitor their antibacterial and antibiofouling activities on different bacterial strains.
It is very interesting to emphasize that C60/PU composite films eradicated almost completely S. flexneri for 1 h. S. flexneri is a Gram-negative intracellular pathogen responsible for bacillary dysentery in humans [53]. Per year, more than 1 million deaths occur due to infections with Shigella spp. The victims are mostly children from the developing world. The pathogenesis of Shigella is based on its ability to invade the colonic epithelium, where it induces severe mucosal inflammation.
We supposed that the antibacterial activity of CPD/PU composite films is predominantly based on ROS generation and further disruption of the bacterial membrane. The C60/PU composite films interacted with bacterial membranes by electrostatic forces, and the production of singlet oxygen induced higher membrane permeation compared with the CPD/PU composite films and further bacteria cell death.
Antibiofouling testing showed that the CPD/PU composite films had potent activity against P. aeruginosa and S. aureus under blue light. The CPD/PU composite films showed better antibiofouling activity against P. aeruginosa compared with our previous results related to carbon quantum dots films deposited by the Langmuir–Blodgett method on glass and Si substrates [54].
Melanin is a critical component of fungal cell walls, which protect fungi from adverse environmental stress [55]. The results showed that CPDs and C60 act differently against A. niger due to different charge transfer, C60 dissolves in toluene and can encapsulate in the very small pores of polyurethane and at the end, the interaction between the wall of A. niger and C60 is more intensive than the interaction between CPDs and membrane wall of A. niger.

5. Conclusions

In this paper, we compared the antibacterial and antibiofouling activities of two types of polymer composite films: CPDs/PU and C60/PU. CPDs were synthesized using the solvothermal method using cheap riboflavin powder as a precursor. AFM analysis showed that these dots had a core–shell structure. CPDs and C60 were encapsulated into polyurethane films using the swelling–encapsulation–shrink method. EFM analysis indicated that the electronic structure of the CPD/PU and C60/PU composite films was related to their ROS generation and antibacterial properties. Both polymer composite films produced ROS: CPD/PU composite films generated both singlet oxygen and hydroxyl radicals, whereas C60/PU composite films generated singlet oxygen only. Antibacterial testing showed strong activity of these composite films against seven bacteria strains and one fungus. The antibiofouling activity of the CPD/PU composite films showed almost full eradication of biofilms of P. aeruginosa and S. aureus under blue light irradiation for 1 h. In this way, both polymer composite films could have a promising future as antibacterial surfaces in hospitals, especially in intensive care and burn units.

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/jfb15030073/s1, Figure S1: (a) FTIR spectra of C60 (black curve) and CPDs (red curve) and (b) FTIR spectra of neat PU (black curve), CPDs/PU (red curve) and C60/PU (green curve). All spectra are displaced for clarity, Figure S2: (a) UV-Vis spectra of C60 (black curve) and CPDs (red curve) and (b) UV-Vis spectra of C60/PU (black curve) and CPDs/PU (red curve) composite films. All UV-Vis spectra were normalized to 1. Table S1: Position of characteristic bonds and shifts (Δ) identified in all samples in cm−1.

Author Contributions

Conceptualization, B.M.T.M. and Z.M.M.; methodology, Z.M.M., M.D.B.F., D.D.M., J.K. and B.M.T.M.; software, Z.M.M. and B.M.T.M.; validation, B.M.T.M., M.D.B.F. and Z.M.M.; formal analysis, Z.M.M. and J.K.; investigation, B.M.T.M. and Z.M.M.; resources, B.M.T.M.; data curation, Z.M.M., M.D.B.F., D.D.M., J.K. and B.M.T.M.; writing—original draft preparation, Z.M.M. and B.M.T.M.; writing—review and editing, B.M.T.M.; visualization, Z.M.M.; supervision, B.M.T.M.; project administration, B.M.T.M.; funding acquisition, B.M.T.M. All authors have read and agreed to the published version of the manuscript.

Funding

This research was supported by the Science Fund of the Republic of Serbia (grant no. #7741955, Are photoactive nanoparticles salvation the global infection threat? PHOTOGUN4MICROBES). This research was also supported by the Ministry of Science, Technological Development and Innovation of the Republic of Serbia (grant number 451-03-66/2024-03/200017). The authors acknowledge the financial support from the Slovenian Research Agency (research core funding no. P2-0082).

Data Availability Statement

The data presented in this study are available on request from the corresponding author.

Acknowledgments

Special thanks to Marija Bogdanović from The Institute of Virology, Vaccines and Sera “Torlak”, who performed antibacterial testing of both types of composites.

Conflicts of Interest

The authors declare no conflicts of interest.

References

  1. Shineh, G.; Mobaraki, M.; Perves Bappy, M.J.; Mills, D.K. Biofilm formation, and related impacts on healthcare, food Processing and packaging, industrial manufacturing, marine industries, and sanitation—A review. Appl. Microbiol. 2023, 3, 629–665. [Google Scholar] [CrossRef]
  2. Percival, L.; Suleman, L.; Vuotto, C.; Donelli, G. Healthcare-associated infections, medical devices and biofilms: Risk, tolerance and control. J. Med. Microbiol 2015, 64, 323–334. [Google Scholar] [CrossRef]
  3. Wißmann, J.E.; Kirchhoff, L.; Brüggemann, Y.; Todt, D.; Steinmann, J.; Steinmann, E. Persistence of pathogens on inanimate surfaces: A narrative review. Microorganisms 2021, 9, 343. [Google Scholar] [CrossRef]
  4. Assefa, M.; Amare, A. Biofilm-associated multi-drug resistance in hospital-acquired infections: A review. Infect. Drug Resist. 2022, 15, 5061–5068. [Google Scholar] [CrossRef]
  5. Cruz-Lopez, F.; Martinez-Melendez, A.; Garza-Gonzalez, E. How does hospital microbiota contribute to healthcare-associated infections? Microorganisms 2023, 11, 192. [Google Scholar] [CrossRef] [PubMed]
  6. Cruz-Lopez, F.; Villarreal-Treviño, L.; Morfin-Otero, R.; Martínez-Meléndez, A.; Camacho-Ortiz, A.; Rodríguez-Noriega, E.; Garza-González, E. Microbial diversity and colonization patterns of two step-down care units from a tertiary care hospital. J. Res. Med. Sci. 2021, 26, 126. [Google Scholar] [CrossRef] [PubMed]
  7. Jabłońska-Trypuć, A.; Makuła, M.; Włodarczyk-Makuła, M.; Wołejko, E.; Wydro, U.; Serra-Majem, L.; Wiater, J. Inanimate surfaces as a source of hospital infections caused by fungi, bacteria and viruses with particular emphasis on SARS-CoV-2. Int. J. Environ. Res. Public Health 2022, 19, 8121. [Google Scholar] [CrossRef]
  8. Kurashige, E.J.O.; Oie, S.; Furukawa, H. Contamination of environmental surfaces by methicillin-resistant Staphylococcus aureus (MRSA) in rooms of inpatients with MRSA-positive body sites. Braz. J. Microbiol. 2016, 47, 703–705. [Google Scholar] [CrossRef]
  9. Fazeli, H.; Akbari, R.; Moghim, S.; Narimani, T.; Arabestani, M.R.; Ghoddousi, A.R. Pseudomonas aeruginosa infections in patients, hospital means, and personnel’s specimens. J. Res. Med. Sci. 2012, 17, 332–337. [Google Scholar]
  10. Huang, L.; Tang, J.; Tian, G.; Tao, H.; Li, Z. Risk factors, outcomes, and predictions of extensively drug-resistant Acinetobacter baumannii nosocomial infections in patients with nervous system diseases. Infect. Drug Resist. 2023, 16, 7327–7337. [Google Scholar] [CrossRef]
  11. Kramer, A.; Assadian, O. Survival of Microorganisms on Inanimate Surfaces. In Use of Biocidal Surfaces for Reduction of Healthcare Acquired Infections; Borkow, G., Ed.; Springer International Publishing: Berlin/Heidelberg, Germany, 2014; pp. 7–26. [Google Scholar] [CrossRef]
  12. Zheng, S.; Bawazir, M.; Dhall, A.; Kim, H.E.; He, L.; Heo, J.; Hwang, G. Implication of surface properties, bacterial motility, and hydrodynamic conditions on bacterial surface sensing and their initial adhesion. Front. Bioeng. Biotechnol. 2021, 9, 643722. [Google Scholar] [CrossRef] [PubMed]
  13. Donlan, R.M. Biofilms: Microbial life on surfaces. Emerg. Infect. Dis. 2002, 8, 881–890. [Google Scholar] [CrossRef]
  14. Yin, W.; Xu, S.; Wang, Y.; Zhang, Y.; Chou, S.H.; Galperin, M.Y.; He, J. Ways to control harmful biofilms: Prevention, inhibition, and eradication. Crit. Rev. Microbiol. 2021, 47, 57–78. [Google Scholar] [CrossRef]
  15. Dai, T.; Huang, Y.; Hamblin, M.R. Photodynamic therapy for localized infections−State of the art. Photodiagn. Photodyn. Ther. 2009, 6, 170–188. [Google Scholar] [CrossRef]
  16. Maisch, T.; Baier, J.; Franz, B.; Maier, M.; Landthaler, M.; Szeimies, R.; Bäumler, W. The role of singlet oxygen and oxygen concentration in photodynamic inactivation of bacteria. Proc. Natl. Acad. Sci. USA 2007, 104, 7223–7228. [Google Scholar] [CrossRef]
  17. Kováčová, M.; Marković, Z.M.; Humpolíček, P.; Mičušík, M.; Švajdlenková, H.; Kleinová, A.; Danko, M.; Kubát, P.; Vajďák, J.; Capáková, Z.; et al. Carbon quantum dots modified polyurethane nanocomposite as effective photocatalytic and antibacterial agents. ACS Biomater. Sci. Eng. 2018, 4, 3983–3993. [Google Scholar] [CrossRef]
  18. Marković, Z.M.; Kováčová, M.; Jeremić, S.R.; Nagy, Š.; Milivojević, D.D.; Kubat, P.; Kleinová, A.; Budimir, M.D.; Mojsin, M.M.; Stevanović, M.J.; et al. Highly efficient antibacterial polymer composites based on hydrophobic riboflavin carbon polymerized dots. Nanomaterials 2022, 12, 4070. [Google Scholar] [CrossRef]
  19. Savelyev, Y.; Gonchar, A.; Movchan, B.; Gornostay, A.; Vozianov, S.; Rudenko, A.; Rozhnova, R.; Travinskaya, T. Antibacterial polyurethane materials with silver and copper nanoparticles. Mater. Proc. 2017, 4, 87–94. [Google Scholar] [CrossRef]
  20. Miranda, C.; Castano, J.; Valdebenito-Rolack, E.; Sanhueza, F.; Toro, R.; Bello-Toledo, H.; Uarac, P.; Saez, L. Copper-polyurethane composite materials: Particle size effect on the physical-chemical and antibacterial properties. Polymers 2020, 12, 1934. [Google Scholar] [CrossRef] [PubMed]
  21. Saleemi, M.A.; Lim, V. Overview of antimicrobial polyurethane-based nanocomposite materials and associated signaling pathways. Eur. Polym. J. 2022, 167, 111087. [Google Scholar] [CrossRef]
  22. Farrokhi, Z.; Ayati, A.; Kanvisi, M.; Sillanpää, M. Recent advance in antibacterial activity of nanoparticles contained polyurethane. J. Appl. Polym. Sci. 2018, 136, 46997. [Google Scholar] [CrossRef]
  23. Ghirardello, M.; Ramos-Soriano, J.; Galan, M.C. Carbon dots as an emergent class of antimicrobial agents. Nanomaterials 2021, 11, 1877. [Google Scholar] [CrossRef] [PubMed]
  24. Zhang, X.; Cong, H.; Yu, B.; Chen, Q. Recent advances of water-soluble fullerene derivatives in biomedical applications. Mini-Rev. Org. Chem. 2019, 16, 92–99. [Google Scholar] [CrossRef]
  25. Díez-Pascual, A.M. State of the art in the antibacterial and antiviral applications of carbon-based polymeric nanocomposites. Int. J. Mol. Sci. 2021, 22, 10511. [Google Scholar] [CrossRef] [PubMed]
  26. Nečas, D.; Klapetek, P. Gwyddion: Open-source software for SPM data analysis. Cent. Eur. J. Phys. 2012, 10, 181–218. [Google Scholar] [CrossRef]
  27. AM-FM Viscoelastic Mapping Mode. Available online: https://afm.oxinst.com/assets/uploads/products/asylum/documents/AM-FM-Viscoelastic-Mapping-Mode-Application-Note.pdf (accessed on 2 February 2024).
  28. Moulder, J.F.; Stickle, W.F.; Sobol, P.E.; Bomben, K.D. Handbook of X-Ray Photoelectron Spectroscopy; Physical Electronics Inc.: Eden Prairie, MN, USA, 1995. [Google Scholar]
  29. Lin, H.; Shen, Y.; Chen, D.; Lin, L.; Wilson, B.C.; Li, B.; Xie, S. Feasibility study on quantitative measurements of singlet oxygen generation using singlet oxygen sensor green. J. Fluoresc. 2013, 23, 41–47. [Google Scholar] [CrossRef] [PubMed]
  30. Entradas, T.; Waldron, S.; Volk, M. The detection sensitivity of commonly used singlet oxygen probes in aqueous environments. J. Photochem. Photobiol. B Biol. 2020, 204, 111787. [Google Scholar] [CrossRef] [PubMed]
  31. Marković, Z.M.; Budimir, M.D.; Danko, M.; Milivojević, D.D.; Kubat, P.; Zmejkoski, D.Z.; Pavlović, V.B.; Mojsin, M.M.; Stevanović, M.J.; Todorović Marković, B.M. Structural, optical, and bioimaging characterization of carbon quantum dots solvothermally synthesized from o-phenylenediamine. Beilstein J. Nanotechnol. 2023, 14, 165–174. [Google Scholar] [CrossRef]
  32. ISO 22196:2007; Plastics—Measurement of Antibacterial Activity on Plastics Surfaces. ISO Central Secretariat: Vernier, Geneva, 2007. Available online: https://www.iso.org/standard/40759.html (accessed on 2 February 2024).
  33. Hansen, M.B.; Nielsen, S.E.; Berg, K.J. Re-examination and further development of a precise and rapid dye method for measuring cell growth/cell kill. Immunol. Methods 1989, 119, 203–210. [Google Scholar] [CrossRef]
  34. Jaiswal, M.; Koul, V. Assessment of multicomponent hydrogel scaffolds of poly(acrylic acid-2-hydroxy ethyl methacrylate)/gelatin for tissue engineering applications. J. Biomater. Appl. 2013, 27, 848–861. [Google Scholar] [CrossRef]
  35. Daniel Frisbie, C. IV.C Electric Force Microscopy (EFM) and Scanning Surface Potential Microscopy (SSPM). In Encyclopedia of Physical Science and Technology; Meyers, R.A., Ed.; Elsevier: New York, NY, USA, 2001. [Google Scholar]
  36. Ong, H.G.; Wang, J. Study of Carbon Nanotube Based Devices Using Scanning Probe Microscope. In Physical and Chemical Properties of Carbon Nanotubes; Suzuki, S., Ed.; IntechOpen: London, UK, 2013. [Google Scholar] [CrossRef]
  37. Patel, S.; Petty, C.W.; Krafcik, K.; Loyola, B.; O’Bryan, G.; Friddle, R.W. Imaging latex–carbon nanotube composites by subsurface electrostatic force microscopy. Nanotechnology 2016, 27, 415705. [Google Scholar] [CrossRef]
  38. Jespersen, T.S.; Nygård, J. Mapping of individual carbon nanotubes in polymer/nanotube composites using electrostatic force microscopy. Appl. Phys. Lett. 2007, 90, 183108. [Google Scholar] [CrossRef]
  39. Govindaraj, P.; Sokolova, A.; Salim, N.; Juodkazis, S.; Fuss, F.K.; Fox, B.; Hameed, N. Distribution states of graphene in polymer nanocomposites: A review. Compos. Part B Eng. 2021, 226, 109353. [Google Scholar] [CrossRef]
  40. Onoe, J.; Nakao, A.; Takeuchi, K. XPS study of a photopolymerized C60 film. Phys. Rev. B 1997, 55, 10051–10056. [Google Scholar] [CrossRef]
  41. Infrared Spectroscopy Absorption Table. Available online: https://chem.libretexts.org/Ancillary_Materials/Reference/Reference_Tables/Spectroscopic_Reference_Tables/Infrared_Spectroscopy_Absorption_Table (accessed on 3 February 2024).
  42. Gao, Y.; Jiao, Y.; Lu, W. Carbon dots with red emission as a fluorescent and colorimetric dual-readout probe for the detection of chromium (VI) and cysteine and its logic gate operation. J. Mater. Chem. B 2018, 6, 6099–6107. [Google Scholar] [CrossRef] [PubMed]
  43. Nguyen, K.G.; Baragau, I.A.; Gromicova, R.; Nicolaev, A.; Thompson, S.A.J.; Rennie, A.; Power, N.P.; Sajjad, M.T. Investigating the effect of N-doping on carbon quantum dots structure, optical properties and metal ion screening. Sci. Rep. 2022, 12, 13806. [Google Scholar] [CrossRef]
  44. Sarkar, S.; Sudolská, M.; Dubecký, M.; Reckmeier, C.J.; Rogach, A.L.; Zbořil, R.; Otyepka, M. Graphitic nitrogen doping in carbon dots causes red-shifted absorption. J. Phys. Chem. C 2016, 120, 1303–1308. [Google Scholar] [CrossRef]
  45. Jovanović, S.; Marković, Z.; Budimir, M.; Prekodravac, J.; Zmejkoski, D.; Kepić, D.; Bonasera, A.; Todorović Marković, B. Lights and Dots toward Therapy—Carbon-based quantum dots as new agents for photodynamic therapy. Pharmaceutics 2023, 15, 1170. [Google Scholar] [CrossRef]
  46. Ge, J.; Lan, M.; Zhou, B.; Liu, W.; Guo, L.; Wang, H.; Jia, Q.; Niu, G.; Huang, X.; Zhou, H.; et al. A Graphene quantum dot photodynamic therapy agent with high singlet oxygen generation. Nat. Commun. 2014, 5, 4596. [Google Scholar] [CrossRef]
  47. Chong, Y.; Ge, C.; Fang, G.; Tian, X.; Ma, X.; Wen, T.; Wamer, W.G.; Chen, C.; Chai, Z.; Yin, J.J. Crossover between anti- and pro-oxidant activities of graphene quantum dots in the absence or presence of light. ACS Nano 2016, 10, 8690–8699. [Google Scholar] [CrossRef]
  48. Hong, Y.; Zeng, J.; Wang, X.; Drlica, K.; Zhao, X. Post-stress bacterial cell death mediated by reactive oxygen species. Proc. Natl. Acad. Sci. USA 2019, 116, 10064–10071. [Google Scholar] [CrossRef]
  49. Colombo, I.; Sangiovanni, E.; Maggio, R.; Mattozzi, C.; Zava, S.; Corbett, Y.; Fumagalli, M.; Carlino, C.; Antonia Corsetto, P.; Scaccabarozzi, D.; et al. HaCaT cells as a reliable in vitro differentiation model to dissect the inflammatory/repair response of human keratinocytes. Mediators Inflamm. 2017, 2017, 7435621. [Google Scholar] [CrossRef]
  50. Hanel, K.H.; Cornelissen, C.; Luscher, B.; Baron, J.M. Cytokines and the skin barrier. Int. J. Mol. Sci. 2013, 14, 6720–6745. [Google Scholar] [CrossRef] [PubMed]
  51. Schurer, N.; Kohne, A.; Schliep, V.; Barlag, K.; Goerz, G. Lipid composition and synthesis of HaCaT cells, an immortalized human keratinocyte line, in comparison with normal human adult keratinocytes. Exp. Dermatol. 1993, 2, 179–185. [Google Scholar] [CrossRef] [PubMed]
  52. Jost, V. Packaging related properties of commercially available biopolymers—An overview of the status quo. eXPRESS Polym. Lett. 2018, 12, 429–435. [Google Scholar] [CrossRef]
  53. Philpott, D.J.; Edgeworth, J.D.; Sansonetti, P.J. The pathogenesis of Shigella flexneri infection: Lessons from in vitro and in vivo studies. Philos. Trans. R. Soc. Lond. B Biol. Sci. 2000, 355, 575–586. [Google Scholar] [CrossRef] [PubMed]
  54. Stanković, N.K.; Bodik, M.; Šiffalovič, P.; Kotlar, M.; Mičušik, M.; Špitalsky, Z.; Danko, M.; Milivojević, D.D.; Kleinova, A.; Kubat, P.; et al. Antibacterial and antibiofouling properties of light triggered fluorescent hydrophobic carbon quantum dots Langmuir−Blodgett thin films. ACS Sustain. Chem. Eng. 2018, 6, 4154–4163. [Google Scholar] [CrossRef]
  55. Xu, X.; Cao, R.; Li, K.; Wan, Q.; Wu, G.; Lin, Y.; Huang, T.; Wen, G. The protective role and mechanism of melanin for Aspergillus niger and Aspergillus flavus against chlorine-based disinfectants. Wat. Res. 2022, 223, 119039. [Google Scholar] [CrossRef]
Jfb 15 00073 g001
Figure 1. Top view AFM images of CPD nanoparticles: (a) height retrace mode, (b) phase retrace mode, (c) viscoelastic measurement of Young’s modulus and (d) profile of Young’s modulus.
Figure 1. Top view AFM images of CPD nanoparticles: (a) height retrace mode, (b) phase retrace mode, (c) viscoelastic measurement of Young’s modulus and (d) profile of Young’s modulus.
Jfb 15 00073 g001
Jfb 15 00073 g002
Figure 2. Top view AFM images of neat PU (a), CPDs/PU (b) and C60/PU (c) composite films. Scale bar is 400 nm.
Figure 2. Top view AFM images of neat PU (a), CPDs/PU (b) and C60/PU (c) composite films. Scale bar is 400 nm.
Jfb 15 00073 g002
Jfb 15 00073 g003
Figure 3. Top view AFM images of surface morphology (left column) and corresponding EFM phase retrace mode images of surface of CPDs (a,b), CPDs/PU (d,e) and C60/PU composite films (g,h). Dark voids represent CPDs themselves (b), and CPDs in the interior of polymer matrix (d) and C60 into the polymer matrix (f). (c,f,i) show profiles of CPDs, CPDs inside PU and C60 in the interior of PU. Tip voltage was 3 V; room humidity was 35%.
Figure 3. Top view AFM images of surface morphology (left column) and corresponding EFM phase retrace mode images of surface of CPDs (a,b), CPDs/PU (d,e) and C60/PU composite films (g,h). Dark voids represent CPDs themselves (b), and CPDs in the interior of polymer matrix (d) and C60 into the polymer matrix (f). (c,f,i) show profiles of CPDs, CPDs inside PU and C60 in the interior of PU. Tip voltage was 3 V; room humidity was 35%.
Jfb 15 00073 g003
Jfb 15 00073 g004
Figure 4. (a) Absorption spectra of SOSG used as fluorescence probe at 530 nm in the presence of CPDs/PU samples, (b) absorption spectra of SOSG at 533 nm in the presence of C60/PU samples, (c) production rate of singlet oxygen of CPD/PU and C60/PU samples vs. time, (d) photobleaching of ABDA in the presence of CPD/PU samples, (e) photobleaching of ABDA in the presence of C60/PU samples. All absorbance spectra of ABDA were recorded at 398 nm, normalized at the start of the irradiation and averaged over several repeat experiments.
Figure 4. (a) Absorption spectra of SOSG used as fluorescence probe at 530 nm in the presence of CPDs/PU samples, (b) absorption spectra of SOSG at 533 nm in the presence of C60/PU samples, (c) production rate of singlet oxygen of CPD/PU and C60/PU samples vs. time, (d) photobleaching of ABDA in the presence of CPD/PU samples, (e) photobleaching of ABDA in the presence of C60/PU samples. All absorbance spectra of ABDA were recorded at 398 nm, normalized at the start of the irradiation and averaged over several repeat experiments.
Jfb 15 00073 g004
Jfb 15 00073 g005
Figure 5. (a) PL intensity spectra of h-TA at time intervals of 0–90 min and (b) PL intensity spectra of h-TA at time intervals of 0–10 min under excitation of 330 nm. Both samples were irradiated with blue light at 470 nm, 3 W.
Figure 5. (a) PL intensity spectra of h-TA at time intervals of 0–90 min and (b) PL intensity spectra of h-TA at time intervals of 0–10 min under excitation of 330 nm. Both samples were irradiated with blue light at 470 nm, 3 W.
Jfb 15 00073 g005
Jfb 15 00073 g006
Figure 6. Antibiofouling effect of CPD/PU and C60/PU composite films on P. aureginosa (a), S. aureus (b) and E. coli (c) bacterial biofilms with and without blue light irradiation for 1 h. Absorbance is an indicator of the quantity of biofilm formed.
Figure 6. Antibiofouling effect of CPD/PU and C60/PU composite films on P. aureginosa (a), S. aureus (b) and E. coli (c) bacterial biofilms with and without blue light irradiation for 1 h. Absorbance is an indicator of the quantity of biofilm formed.
Jfb 15 00073 g006
Jfb 15 00073 g007
Figure 7. Cytotoxicity of PU (control), CPD/PU and C60/PU composite film samples without blue light irradiation determined as a percentage of viable HaCaT cells. The dashed lines highlight the limits of viability according to EN ISO 10993-5: viability >80 corresponds to no cytotoxicity, >60–80 mild cytotoxicity, >40–60 moderate toxicity and <40 severe toxicity.
Figure 7. Cytotoxicity of PU (control), CPD/PU and C60/PU composite film samples without blue light irradiation determined as a percentage of viable HaCaT cells. The dashed lines highlight the limits of viability according to EN ISO 10993-5: viability >80 corresponds to no cytotoxicity, >60–80 mild cytotoxicity, >40–60 moderate toxicity and <40 severe toxicity.
Jfb 15 00073 g007
Table 1. Elements identified in the CPD and C60 samples in At%.
Table 1. Elements identified in the CPD and C60 samples in At%.
CPDC60
ElementAt%At%
C 1 s83.190.0
O 1 s7.310.0
N 1 s9.60.0
Table 2. Characteristic bonds detected in the CPD and C60 samples and relative concentration of these bonds %.
Table 2. Characteristic bonds detected in the CPD and C60 samples and relative concentration of these bonds %.
Characteristic BondBinding Energy (eV)Relative Concentration (%)Characteristic BondBinding Energy (eV)Relative Concentration (%)
CPDs C60
C 1 s peak C-C/C-H284.580C 1 s peak C-C/C-H284.579
C 1 s peak C=O286.520C 1 s peak C-O/C-OH285.920
O 1 s peak C=O531.4100C1 s peak C-O/C-OH288.71
N 1 s peak pyridinic398.745O 1 s peak O-H 532.287
N 1 s peak pyrrolic399.949O 1 s peak C-O/H2O 533.313
N 1 s peak C=N-C396.46---
Table 3. Number of viable bacteria colonies after treatment with the CPD/PU and C60/PU composite films in the presence and absence of blue light irradiation.
Table 3. Number of viable bacteria colonies after treatment with the CPD/PU and C60/PU composite films in the presence and absence of blue light irradiation.
Bacteria StrainsIrradiated,
Incubated
N (cell/cm2)		Nonirradiated,
Incubated
N (cell/cm2)		RIrradiated,
Incubated
N (cell/cm2)		Nonirradiated,
Incubated
N (cell/cm2)		R
CPDs/PU C60/PU
K. pneumoniae005.45005.45
P. mirabilis020 × 1065.52005.52
S. enterica05 × 1074.8102 × 1074.81
E. faecalis010 × 1055.5306 × 1055.53
E. epidermis004.5502 × 1060.11
S. flexneri64 × 10282 × 1042.107.6 × 1039.8 × 1052.12
P. aeruginosa070 × 1054.9501 × 1054.95
A. niger8.7 × 1021 × 1052.06005.47
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Marković, Z.M.; Budimir Filimonović, M.D.; Milivojević, D.D.; Kovač, J.; Todorović Marković, B.M. Antibacterial and Antibiofouling Activities of Carbon Polymerized Dots/Polyurethane and C60/Polyurethane Composite Films. J. Funct. Biomater. 2024, 15, 73. https://doi.org/10.3390/jfb15030073

AMA Style

Marković ZM, Budimir Filimonović MD, Milivojević DD, Kovač J, Todorović Marković BM. Antibacterial and Antibiofouling Activities of Carbon Polymerized Dots/Polyurethane and C60/Polyurethane Composite Films. Journal of Functional Biomaterials. 2024; 15(3):73. https://doi.org/10.3390/jfb15030073

Chicago/Turabian Style

Marković, Zoran M., Milica D. Budimir Filimonović, Dušan D. Milivojević, Janez Kovač, and Biljana M. Todorović Marković. 2024. "Antibacterial and Antibiofouling Activities of Carbon Polymerized Dots/Polyurethane and C60/Polyurethane Composite Films" Journal of Functional Biomaterials 15, no. 3: 73. https://doi.org/10.3390/jfb15030073

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop