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Photoinactivation of S. aureus biofilms using porphyrin conjugates with green-synthesized TiO2 immobilized on waste polystyrene

Nonkululeko Malomanea, Nkgameleng K. Mokhonoanaa, Christian I. Nkangab, Ojodomo J. Achaduc, Richard M. Moutloalia and Muthumuni Managa*a
aInstitute for Nanotechnology and Water Sustainability (iNanoWS), Florida Campus, College of Science, Engineering and Technology, University of South Africa, Johannesburg 1710, South Africa. E-mail: managme@unisa.ac.za
bCentre de Recherche en Nanotechnologies Appliquées aux Produits Naturels (CReNAPN), Department of Medicinal Chemistry and Pharmacognosy, Faculty of Pharmaceutical Sciences, University of Kinshasa, B.P. 212, Kinshasa XI, Democratic Republic of the Congo
cSchool of Health and Life Sciences &, National Horizon Centre, Teesside University, Tees Valley, Middlesbrough TS1 3BX, UK

Received 4th January 2026 , Accepted 22nd April 2026

First published on 20th May 2026


Abstract

Waterborne infections remain a global concern, exacerbated by biofilms in water storage systems that resist chlorine disinfection. In this study, antimicrobial photodynamic inactivation was investigated using novel porphyrin-TiO2 nanoconjugates prepared from green-derived TiO2 nanoparticles using Citrus sinensis extracts and immobilized on waste polystyrene (PS) for the first time. Metal-free 5,10,15-tris(4-bromophenyl)-20-(4-carboxyphenyl)porphyrin (1) and its ClIn(III) derivative (2) were conjugated to TiO2, then immobilized on PS. Characterization by FTIR, EDX, TGA, SEM, TEM, and UV-vis confirmed successful formation of thermally stable and spherical nanostructures. Moreover, photophysical studies showed that metalation reduced fluorescence quantum yield (ΦF) from 0.01 (1) to <0.01 (2) due to heavy atom effect) while boosting singlet oxygen yield ((ΦΔ) from 0.68 (1) to 0.85 (2)–0.90 (2-TP). Free 2-TP achieved 0.0006% S. aureus survival percentage while PS-immobilized versions reached 2.5% under 30 minutes visible light exposure. These sustainable, high-efficiency materials advance biofilm-resistant water treatment for resource-limited settings.


1 Introduction

Waterborne infections continue to threaten human health globally, contributing to 1.4 million unsafe Water, Sanitation, and Hygiene (WASH)-related annual deaths worldwide.1 In Sub-Saharan Africa, this equates to 115 deaths per hour from poor sanitation and contaminated water.2 Contributing factors include bacteria such as S. aureus, prevalent in stored household water and driving antimicrobial resistance.3 A critical, yet understudied factor that perpetrates the spread of waterborne infections, is the biofilm formation on the surfaces of water storage systems.4 Households from resource-constrained areas, such as rural settlements, are at risk of waterborne diseases.5 They collect and store water that may already be contaminated with pathogenic bacteria or can be contaminated during collection, transportation, storage and use. Suspended bacteria attach to the surface inside and to each other during storage using self-made extracellular substances (EPS).6 The bacteria then multiply and detach in a continuous process. Besides offering protection to bacteria, biofilms play a significant role in lowering the efficiency of disinfectants such as chlorine.6,7 They also perpetrate the development and spread of resistance within the bacterial community.8 This greatly deteriorates water quality and necessitates the development of new water disinfection methods.

Antimicrobial photodynamic inactivation (aPDI) has shown great potential for inactivation of bacteria in water.9 In this technique, microorganisms are inactivated by shining light on a photosensitizer that generates reactive oxygen species, causing oxidative stress to the microbe.10 Research on the optimization of photosensitizers to improve their properties is topical. An ideal photosensitizer should produce reactive oxygen species efficiently to cause microbial cell death within a short space of time.6,11 Porphyrins with bromine halogen substituents and diamagnetic heavy metals such as indium have been found to improve aPDI efficiency due to heavy atom effect.12 Furthermore, several studies have shown that adsorption of porphyrins onto UV light active TiO2 nanoparticles improves their overall performance as photosensitizers.13,14 This is achieved by the ability of porphyrins to enhance the absorbance of the overall system in the visible range, as well as improve charge separation of TiO2, thus improving the antimicrobial activity.15 In addition to these photocatalytic enhancements, green synthesized TiO2 nanoparticles alone have been reported to have intrinsic antimicrobial properties, with greater performance than conventionally synthesized TiO2 nanoparticles without any light against S. aureus, E. coli and P. aeruginosa.16

Many light-driven studies utilized TiO2-porphyrin in suspension.17–19 However, this poses risk of photosensitizer leaching and secondary contamination of water and may require additional steps of separation and recovery of the nanoparticles after disinfection.6 To foster real-life applications in the disinfection of water storage systems, studies have used supports such as quartz wool, polyvinylpyrrolidone, polyactic acid, bentonite and chitosan.13,20–22 In addition to this, another study reported that polystyrene (PS) polymer provides stable support to other porphyrin conjugates in electrospun nanofibers.23

In this study, the photophysical and photodynamic antimicrobial properties of previously reported 5,10,15-tris-(4-bromopheyl)-20-(4-carboxyphenyl)porphyrin (1) (Scheme 1) and its indium chloride derivative (2) adsorbed onto green synthesized TiO2 nanoparticles using orange fruit (Citrus sinensis) peel extract (T1) and juice (TP) were explored against environmental S. aureus biofilms.15,24 These porphyrin-TiO2 conjugates represent novel combinations, which were physically immobilized, for the first time, onto waste PS from used PS cups. Waste PS was chosen in contribution to climate change mitigation strategies as it poses a significant environmental health issue due to its non-biodegradable characteristic. The non-biodegradable property of PS serves as an advantage in this study so that the immobilized photosensitizers do not get degraded by the microbes during inactivation.


image file: d6ra00069j-s1.tif
Scheme 1 Chemical structures as-synthesized porphyrins labelled 5,10,15-tris-(4-bromopheyl)-20-(4-carboxyphenyl) porphyrin (1) and ClIn(III) 5,10,15-tris-(4-bromopheyl)-20-(4-carboxyphenyl)porphyrin (2).

2 Experimental

2.1 Conjugation of TiO2 nanoparticles with 1 and 2

Compounds 1, 2, TJ and TP were synthesized, purified and characterized as recently reported.15,24 Metal-free and In(III) porphyrins were conjugated non-covalently with TiO2 nanoparticles following reported procedures.25 1 or 2 (0.025 g) was dissolved in DMF (10 mL), followed by addition of 100 mg TP or TJ. The mixture was stirred for 24 hours at 50 °C to facilitate adsorption of the porphyrin molecules onto the surface of TiO2 nanoparticles. The conjugates were washed several times with ethanol until the washing solution became clear. The conjugates collected via centrifugation were then air-dried overnight at room temperature. The conjugates were labelled 1-TP, 1-TJ for the metal free porphyrin conjugates with TiO2 nanoparticles synthesized from orange peel extract and orange juice, respectively, and 2-TP, 2-TJ for the In(III) porphyrin conjugates.

2.2 Immobilization onto PS waste

2.5 g PS was dissolved into a mixture of chloroform and DMF (1[thin space (1/6-em)]:[thin space (1/6-em)]3), followed by the addition of the photosensitizer (1, 2, TP, TJ, 1-TP, 1-TJ, 2-TP, or 2-TJ) (0.025 mg) and stirring for 30 minutes until a homogeneous mixture was obtained (Scheme 2). This was then poured into glass Petri dishes, and the solvents were allowed to evaporate in air.
image file: d6ra00069j-s2.tif
Scheme 2 Immobilization of the photosensitizers (1, 2, TP, TJ, 1-TP, 1-TJ, 2-TP, or 2-TJ) onto PS waste.

2.3 Photoinactivation studies

2.3.1 Sampling and bacterial isolation. Water samples were collected from a pond at the University of South Africa, Florida campus located in Gauteng, South Africa, using sterile 250 mL glass water sampling bottles. The open pond is stagnant and mimics household water storage conditions, vulnerable to contamination by airborne microbes, bird faeces as well as physical human activities. Prior to sampling, the bottles were thoroughly washed with soap and water and then sterilized by autoclaving for 15 min at 120 °C. On-site physical parameters (pH, conductivity, TDS, turbidity) were measured and S. aureus bacteria were isolated from the water immediately using mannitol salt agar plates by incubating for 48 h at 37 °C. Sequential streaking ensured formation of pure yellow colonies (mannitol fermentation) in mannitol salt agar. The full bacterial characterization (morphology, Gram stain, catalase, 16 s rRNA sanger sequencing for characterization of the bacteria are detailed in the SI.

Prior to inactivation, 30% glycerol stock solution of S. aureus previously isolated (SI) and stored at −20 °C freezer was placed at room temperature to thaw. A full loop of S. aureus stock was aseptically streaked onto mannitol salt agar plate and incubated at 37 °C for 24 hours to obtain fresh bacterial culture. Subsequently, a fresh bacterial stock solution was prepared by inoculating in nutrient broth (6 mL) and incubating (24 h, 37 °C, 200 rpm shaking). When the optical density (OD) of the bacteria at 600 nm reached 0.8, the bacteria were then centrifuged at 4000 rpm for 5 minutes and washed twice with Phosphate-buffered saline (PBS) to remove the broth. The supernatant was decanted, and pellet was stored in 100 mL PBS at a 10−2 dilution factor at −2 °C. The working concentration of the bacteria was optimized by serial dilution plating (10−7 dilution factor in PBS), until less than 300 colonies were obtained in mannitol salt agar.

2.3.2 aPDI studies against freely suspended bacteria using free materials. The aPDI studies were conducted using the reported procedures with modifications.23,26 The colony counting method gave inconsistent unreliable results, therefore, the optical density method (turbimetric analysis) was used to determine the efficiency of the photosensitizers. Photosensitizer concentration optimization was done by exposing the bacteria to 0.05, 0.10, 0.25, 0.5 and 1.0 mg mL−1 of the photosensitizer and 0.25 mg mL−1 was chosen as optimal concentration. Photosensitizer stocks (0.25 mg mL−1); 1, 2, TP, TJ, 1-TP, 1-TJ, 2-TP, and 2-TJ were then prepared in PBS. 150 µL aliquots of the bacterial suspension in PBS were added into sterile 12-well microplates, followed by 100 µL aliquots of each photosensitizer. The initial absorbance of the bacteria was taken using a spectrophotometer. For each experiment, two sets of 12-well plates with similar contents were prepared for dark and light experiments, respectively, and the experiments were performed in triplicates.

Both plates were subjected to a 60-minutes aerobic pre-incubation period in the dark at 37 °C to allow localization of the photosensitizers.27 One plate was subjected to irradiation for 30 minutes, while the other was left in the dark for the same period, with 5 minutes sampling intervals. 100 µL bacteria-photosensitizer suspension was taken out and added to 96-plates, followed by addition of 150 µL nutrient broth and incubation (24 h, 37 °C) in a rotary shaker. The final concentration of the bacteria was determined by checking the absorbance. The controls without photosensitizers were used to correct the viable bacteria. An LED-mounted irradiation chamber equipped with M415L4 LED with a continuous irradiance yielding a maximum of 15.6 µW mm−2 was used. The survival percentage was calculated using the formula:

 
image file: d6ra00069j-t1.tif(1)
where AT is the absorbance of the bacteria after inactivation, AB is the absorbance of the photosensitizer control without any bacteria, and AC is the absorbance of the control bacteria without any photosensitizer.

2.3.3 aPDI studies against biofilm bacteria using free materials. The antibacterial activities of 1, 2, TP, TJ, 1-TP, 1-TJ, 2-TP, and 2-TJ as well as bare-PS were investigated using single-species bacterial biofilms of S. aureus following the reported protocol.28 The bacterial inoculate was prepared using Tryptic soy broth, and 100 µL suspension was placed in 96-well plates and allowing a 5-days incubation period at 37 °C. To encourage biofilm growth, unbound cells were rinsed with PBS, and the wells were replenished with new Tryptic soy after 18 h. The biofilm-coated wells were subjected to three PBS washes and a 30-minutes air drying period.

For illumination, 1.0 mg mL−1 of each photosensitizer, optimized as described above, was placed into biofilm-coated wells and incubated for 1 hour at 37 °C in a rotary shaker.29 The wells were then illuminated for 30 minutes at 5 minutes sampling intervals times. Following this, the cells were stained with 1% aqueous crystal violet (CV) solution, and excess CV removed by three PBS washes after 30 min, and fresh Tryptic soy broth added into the wells to determine the survival fraction of biofilms by checking their absorbance and comparing them to those without photosensitizers.30 On the other hand, PBS was added to dilute the samples maintained in the dark and then each solution was carefully inoculated on Tryptic soy broth, followed by 18 h incubation at 37 °C. The controls without photosensitizers were used to correct the viable bacteria and the optical densities of the viable bacteria were calculated at 600 nm. Each of these experiments were done in triplicates.

2.3.4 Photoinactivation of freely suspended bacteria using immobilized photosensitizers. The photodynamic antimicrobial activity of the photosensitizers immobilized onto waste PS, 1-PS, 2-PS, TP-PS, TJ-PS, 1-TP-PS, 1-TJ-PS, 2-TP-PS, and 2-TJ-PS, were examined against environmental S. aureus in suspension according to a modified procedure adopted from literature.31 PS alone was used as negative control. In a typical experiment, one 1 × 1 cm2 piece of each of the immobilized photosensitizers was separately placed in sterile 12-well microplates. 150 µL PBS suspension of was added into the wells containing the photosensitizers onto PS. After incubation of 60 min, the wells were exposed to a light illumination for 30 min, while the other pairs of wells were left in the dark for the same duration. For each experiment, two sets of 12-well plates with similar contents were prepared for dark and light experiments, respectively, and the experiments were performed in triplicates. Afterwards, the immobilized photosensitizers from all wells were taken out of the bacterial solution and were placed into 5 mL of sterilized PBS solution. The solution was shaken vigorously for 1 min. 100 µL bacteria was taken into 96 well plates, followed by addition of 150 µL nutrient broth and incubated for 24 h in a rotary shaker at 37 °C. The final concentration of the bacteria was determined by checking the absorbance. The bacterial solutions without immobilized photosensitizers were used as negative controls to correct the viable bacteria and the optical densities of the viable bacteria were calculated at 600 nm. The survival percentage was calculated using the eqn (1).
2.3.5 Photoinactivation of biofilm bacteria using immobilized photosensitizers. The photodynamic antimicrobial activity of the photosensitizers immobilized onto waste PS, 1-PS, 2-PS, TP-PS, TJ-PS, 1-TP-PS, 1-TJ-PS, 2-TP-PS, and 2-TJ-PS, were examined against single species S. aureus biofilms. The biofilms were prepared and illuminated as described above. In a typical experiment, one 1 × 1 cm2 piece of each of the immobilized photosensitizer was separately placed in biofilm coated wells. For each experiment, two sets of 96-well plates with similar contents were prepared for dark and light experiments, respectively, and the experiments were performed in triplicates. After incubation of 60 min, the wells were exposed to a light illumination for 30 min with 5 minutes sampling intervals while the other pairs of wells were left in the dark for the same duration. Afterwards, the immobilized photosensitizers were removed from all wells. Following this, the cells were stained with 1% aqueous CV solution, and excess CV removed by three PBS washes after 30 min, and fresh PBS added into the wells to determine the survival fraction of biofilms by checking their absorbance and comparing them to those without photosensitizers.30 On the other hand, PBS was added to dilute the samples maintained in the dark and then each solution was carefully inoculated on agar plates, followed by 18 h incubation at 37 °C. The controls without photosensitizers were used to correct the viable bacteria and the optical densities of the viable bacteria were calculated at 600 nm. Each of these experiments were done in triplicates.

3 Results and discussion

3.1 Fourier transform infrared spectroscopy (FTIR)

The functional groups within the materials were studied using FTIR. Fig. 1 shows the FTIR spectra of PS, TJ, 2-TJ, 2-TJ-PS as well as that of previously reported 2 (ref. 24) as examples. The results for TJ showed a strong peak below 1000 cm−1, indicating the presence of Ti–O bonds in the anatase phase of TiO2.32 Broad absorption bands at 3400 and 1635 cm−1 revealed hydroxyl groups (O–H or Ti–OH) due to water moisture adsorbed on the TiO2 surface.33 Notably, nanoparticles TP and TJ exhibited an additional peak at 1392 cm−1 (C–C/C[double bond, length as m-dash]C), attributed to organic residues from calcination, consistent with previous findings.16 The FTIR spectra of 2 shows characteristic peaks for the carboxylic acid group (1691 cm−1) and pyrrole ring (1510, 1424, 1280, and 1010 cm−1). After conjugation, similar changes were observed for all conjugates, with decreased intensity and shifted C[double bond, length as m-dash]O and C–O bands. Two new intense bands emerged at 1650 and 1394 cm−1, indicating the formation of carboxylate species (ν(–CO2), due to chemisorption onto the TiO2 surface. This interaction may contribute to the enhanced activity of the conjugated systems, consistent with previous reports.34
image file: d6ra00069j-f1.tif
Fig. 1 FTIR spectra of PS, 2, TJ, 2-TJ, 2-TJ-PS as an example.

For PS, the C[double bond, length as m-dash]C peaks appear at 1600, 1492, and 1451 cm−1, indicating the presence of expected benzene rings in PS.35 The transmission band at 3025 cm−1 corresponds to the stretching vibrational modes of aromatic C–H groups, and the peak at 2941 cm−1 corresponds to vibrational modes of C–H2 due to methylene groups.35,36 Typical out-of-plane bending vibration C–H peaks occur at 754 and 694 cm−1, confirming only one substituent in the benzene ring.36 These peaks are not present in 2-TJ and TJ alone and appear to overlap with Ti–O peaks in 2-TJ-PS, confirming the presence of the conjugates on the PS. A previous study by Naik et al.37 found that immobilizing of iron and cobalt metalloporphyrins onto PS physically does not significantly alter its FTIR or UV-vis spectra but causes prevalence of PS peaks. Similarly, this study observed that the conjugates' C[double bond, length as m-dash]O/Ti–OH groups are masked, likely due to the dominant C[double bond, length as m-dash]C peak of PS at 1671 cm−1. This suggests that the porphyrins, TiO2, and their conjugates retain their original structure and are uniformly distributed within the PS matrix. As a result, they are likely to maintain their photosensitization properties during aPDI.38

3.2 X-ray diffraction (XRD)

XRD is an analytical tool used to identify the crystal structure of materials, which is essential for understanding their photocatalytic properties. Different crystal structures can significantly impact a material's photoinactivation efficiency.39 High crystallinity of a material in photocatalysis is normally attributed to high photocatalytic activity.40 In this study, XRD analysis were investigated to inspect the crystal properties of the nanoparticles, as well as the effect of porphyrin on the crystal structure of TiO2. Fig. S1 confirms the amorphous nature of 1 and 2. The XRD patterns of the nanoparticles and conjugates are shown in Fig. 2. TP and TJ showed diffraction peaks (JCPDS 00-001-0562) at 25.5, 38.3, 48.3, 54.2, 55.1, 62.9, 69.3, 70.4, and 75.6° 2θ, confirming anatase TiO2.41 Moreover, there were no changes in the peaks of TiO2 when conjugated to 1 as shown in the diffraction patterns of 1-TP and 1-TJ. This suggests that the porphyrin had no significant influence on the crystal structure of the TiO2 nanoparticles.18
image file: d6ra00069j-f2.tif
Fig. 2 XRD patterns of TP, TJ, 1-TP, and 1-TJ as an example.

3.3 Thermogravimetric analysis (TGA)

Thermogravimetric analysis was used to study the stability of the synthesized molecules. As observed, the thermograms (Fig. 3) of the porphyrins alone indicate a significant gradual percentage loss of the porphyrin molecules up to 45 and 50 °C for 1 and 2 at 900 °C, respectively. However, the TiO2 nanoparticles alone show great thermal stability up until 900 °C, with just less than 4% weight loss due to absorbed water molecules. The conjugates, although with a slightly lower stability than TiO2, show improved thermal stability (12, 7, 5, and 5% weight loss at 900 °C for 2-TP, 2-TJ, 1-TP and 1-TJ, respectively) compared to the porphyrins.
image file: d6ra00069j-f3.tif
Fig. 3 TGA thermograms grams for 1, 2, TP, TJ, 1-TP, 1-TJ, 2-TP and 2-TJ.

3.4 Transmission electron microscopy (TEM)

TEM was used to study the morphological analysis of the synthesized materials. Fig. 4 shows the TEM micrograms of TJ and 2-TJ as examples. It was observed that TJ has a spherical morphology which is aggregated when in combination with porphyrin. The average sizes were calculated using image-J software and were found to be 13.71 and 13.27 nm TP and TJ, respectively. These sizes increased slightly during conjugation to 15.03, 17.30, 17.44, and 18.21 for 1-TP, 1-TJ, 2-TP, and 2-TJ, respectively. This observation was anticipated, as it aligns with the expected interaction between the porphyrin molecules and the nanoparticles, leading to a subtle alteration in their morphology.19,42 However, the aggregation may also be due to the sample preparation method during the TEM analysis.43
image file: d6ra00069j-f4.tif
Fig. 4 TEM micrograms for TJ (a) and 2-TJ as examples (b).

3.5 Scanning electron microscopy (SEM)

SEM was used to examine the produced nanomaterials' morphology. Research has revealed that the shape and size of nanomaterials are influenced by the synthetic route and play a role in the efficiency of the material.44 As observed (Fig. S1), the TJ and 2-TJ confirmed the agglomerated spherical morphology of the free materials as observed in TEM. Fig. 5(a–d) shows the SEM images of the porphyrins, TiO2 nanoparticles and conjugates immobilized onto expanded porphyrin. PS (a), 2-PS (b), TJ-PS (c), and 2-TJ-PS were used as examples. The images of the immobilized materials show porous microvoid PS with a clear presence of the nanoparticles on the surface, confirming successful immobilization. The nanoparticles are exposed on the surface of PS, which maximises the amount of light they can receive during aPDI.
image file: d6ra00069j-f5.tif
Fig. 5 SEM micrograms for PS (a), 2-PS (b), TJ-PS (c), and 2-TJ-PS (d) as examples.

3.6 Energy dispersive X-ray spectroscopy (EDX)

The elemental composition of the synthesized materials was studied using the EDX. Fig. S2 shows the EDX spectra of the free materials TP, TJ, 2-TP and 2-TJ. The elements observed are Ti, O, C, Br, In, C and Cl as expected for 2-TP and 2-TJ. The Au is due to the gold coating used during sample preparation for analysis. Furthermore, the EDX spectra of the immobilized materials (Fig. 6) confirmed the presence of all expected elements as described above for the pristine materials. This is accompanied by a strong intense carbon (C) peak which is typical for carbonous polymers.
image file: d6ra00069j-f6.tif
Fig. 6 EDX spectra of PS (a), TP- PS (b), 2-PS (c), and 2-TP-PS (d) as examples.

3.7 UV-vis spectrophotometry

This study employed UV-vis spectrophotometry to investigate the light absorbance of synthesized materials. Fig. 7 shows the absorbance of TP, 1-TP, as well as 2-TP as examples. The absorption of TP is in the UV range as expected due to large bandgap energy. However, the incorporation of porphyrin onto TiO2 nanoparticles resulted in an additional peak in the visible range, indicating successful adsorption. The strong intense Soret band of 1 was previously found to lie at 418 nm, and that of the metalated 2 at 428 nm.15 In this study, the Soret band of the unmetalated porphyrin conjugate 1-TP was observed at the same wavelength as its unconjugated counterpart (1, 418 nm). There was a 4-unit red shift to 424 nm for 2-TP, attributed to the interaction between TiO2 and porphyrin. The results align with previous reports on interaction of porphyrin-TiO2 conjugates.13
image file: d6ra00069j-f7.tif
Fig. 7 Solid-state UV-vis absorption spectra of TP, 1-TP and 2-TP.

3.8 Photophysical properties

3.8.1 Fluorescence emission spectra. Fluorescence emission spectra measurements were performed in DMF, exciting at 430 nm. Fig. 8a and b show the S1 → S0 fluorescence of 1, 2, 1-TJ, and 2-TJ which exhibit distinct differences in their emission profiles. All the complexes show two typical fluorescence peaks of porphyrins.45 The metal-free porphyrin 1 displayed strong intense peaks around 660 nm for Q(0,0), accompanied by secondary peak of lower intensity at around 725 and 722 nm for Q(0,1) for 1 and 2, respectively.46 In contrast, there was an observed blue-shift in the emission profile of 2 with peaks appearing at 622 nm (strong intense) and 676 nm (less intense). This differences in the emission wavelengths may be due to the substantial change in the electronic structure and photophysical properties of the porphyrin macrocycle, likely due to the influence of the indium metal centre on the ligand's excited-state dynamics.
image file: d6ra00069j-f8.tif
Fig. 8 Fluorescence emission spectra of 1 and 2 (a), and (b) 1-TJ and 2-TJ as an example for the conjugates.

The fluorescence emission profiles of the conjugates are demonstrated in Fig. 8b using 1-TJ and 2-TJ as examples. The spectra still showed the two characteristic peaks as in the case of the porphyrins alone, however, the low intense peak for 2-TJ appeared to have even lower intensity. The characteristic high and less intense peaks were observed at 652 and 716 nm for 1-TJ and at 776 and 728 nm for 2-TJ, respectively.

3.8.2 Fluorescence quantum yield (ΦF) and lifetime (τF). When porphyrins' electrons get excited, they can either undergo intersystem crossing or go back to ground state through emission. ΦF is a measure of the efficiency of the molecule to emit light through fluorescence.26 Whereas τF is the average time that a molecule spends in its excited state before it relaxes and returns to ground state through photon emission. The fluorescence decay curves (Fig. S3) and τF of the synthesized materials were determined using time-correlated single photon counting (TCSPC). In this study, ΦF of 1 in Table 1 was measured to be 0.01 and τF being 5.78 ns, these values decrease upon introduction of the indium metal, with ΦF being <0.01 and τF being 3.78 ns. This effect is due to the ability of In heavy metal to stabilize the excited state, thus quenching fluorescence and promoting intersystem crossing.45 Furthermore, conjugation caused a slight increase in the ΦF of the conjugates with 1, achieving 0.02 and 0.022 for 1-TP and 1-TJ, respectively. However, there was a decrease in the ΦF of the conjugates with 2 as expected. On the other hand, the values of the τF decreased for all conjugates with the lowest ΦF (0.001) observed for both 2-TP and 2-TJ and lowest τF (1.19 ns) observed for 2-TJ. The values, however, were lower than what has been reported on ΦF of TiO2 alone (0.20) from 330–370 nm in an alcoholic medium.47
Table 1 Photophysical parameters of the synthesized materials
Material τF (ns) ΦF ΦΔ (±0.01)
1 5.78 0.01 0.68
2 3.78 <0.01 0.83
1-TP 1.96 0.02 0.74
1-TJ 2.13 0.022 0.74
2-TP 1.37 0.001 0.90
2-TJ 1.19 0.001 0.89


3.8.3 Singlet oxygen quantum yield (ΦΔ). At the excited triplet state, when porphyrin transfers its energy to ground state molecular oxygen it produces singlet oxygen.23 In aPDI, the aim is to have photosensitizers that produce ΦΔ enough to inactivate bacteria in a short space of time.6 The ΦΔ was determined using a standard solution of TPP and ZnTPP in DMF as a reference. The ΦΔ for 1 and 2 were reported to be 0.68 and 0.83, respectively, using TCSPC on burst mode. This confirms that indium induces heavy atom effect that improves the production of reactive oxygen species. In the conjugated materials, higher ΦΔ were observed, the highest achieved was with the 2-TP conjugate showing a value of 0.90. These values were higher than what has been reported on ΦΔ of TiO2 alone (0.12–0.38).13,48 This improvement is desirable for light activated reactions. Fig. S4 shows the phosphorescence decay curve for the determination of ΦΔ of 2 as an example.

3.9 Antimicrobial studies

3.9.1 Physical parameters of the pond water sample and presumptive S. aureus characteristics. Water samples, collected from the University of South Africa's Florida Campus, were analysed on-site for physical parameters (Table 2), revealing temperature, pH, conductivity, total dissolved solids, and turbidity levels all fell within WHO drinking water standards, yet harboured viable S. aureus. Fig. 9a shows positive results for presumptive S. aureus on mannitol salt agar plate, characterised by a golden yellow colour and colour changes of the mannitol salt agar from red to yellowish orange (mannitol fermentation). The gram staining results (Fig. 9b) showed that the bacteria were Gram positive and cocci shaped in single and even paired in chains. Fig. 9c revealed a positive catalase test of the bacteria indicated by the presence of bubbles. All the morphological characterization and catalase test matched S. aureus.
Table 2 Physical parameters of the water samples collected at a pond at UNISA, Florida campus
Site name Temperature (°C) pH Conductivity Total dissolved solids (ppm) Turbidity
Pond water 13.5 ± 0.5 8.29 ± 0.2 833 ± 3.2 418 ± 1.9 0.00 ± 0.0



image file: d6ra00069j-f9.tif
Fig. 9 Presumptive S. aureus colonies on mannitol salt agar after steaking and incubating for 24 hours at 37 °C (a), presumptive S. aureus gram staining results viewed under Olympus CX23 microscopy at 100× oil objective (b), and catalase test results of presumptive S. aureus (c).
3.9.2 Gel electrophoresis and CF-01 sanger sequencing results. Gel electrophoresis is a technique that used for separating molecules by size and charge using an electric field.49 It is used to separate DNA, RNA, or proteins. In this study, DNA extraction was conducted, followed by PCR, and gel-electrophoresis was then employed to separate PCR amplicons of S. aureus samples. Fig. 10 shows the results from gel electrophoresis which indicate that the DNA was present, and that PCR was successful. No contamination was observed in the samples. Furthermore, the data matched the 16S rRNA gene with a band at 1500 base pairs.50
image file: d6ra00069j-f10.tif
Fig. 10 Gel electrophoresis results. 1 KB MW is the 1 kb DNA ladder, 1% agarose, 1xTEA used, S1 and S2 are the DNA amplicons samples in duplicates, Pos2 and Neg are the positive and negative controls (S. aureus). The numbers on the right represent the base pairs.

The 16S rRNA Sanger sequencing results (Fig. 11) confirmed that the isolated presumptive bacteria were indeed S. aureus. The results were analysed using Geneious prime software. All the top hit results from NCBI BAST analysis, when compared to the submitted DNA query sequence, matched S. aureus. The query coverage and percentage identity for all the isolates after NCBI BAST analysis were 100% (Table 3) indicating a strong match between the query sequences and matched one in the NCBI. All the query sequences had the expected value (E value) of zero, indicating good quality of sequencing alignment. The 16S rRNA Sanger sequencing results confirmed that the isolated bacteria were S. aureus.


image file: d6ra00069j-f11.tif
Fig. 11 CF-01 Sanger sequencing results.
Table 3 Presumptive and sanger sequencing results obtained for the S. aureus used in this study
Sample Presumptive bacteria Identified bacteria Query coverage % Identity Expected value
1 S. aureus S. aureus 100% 100 0


3.9.3 aPDI results in suspended bacteria using free photosensitizers. All the aPDI experiments were performed using in photosensitizer materials suspended in PBS. For assurance, validation, and reliability of the results, aPDI studies were conducted in triplicates. Environmental S. aureus was employed as Gram-positive bacteria to study the aPDI activity of the synthesized materials. A lower survival percentage after light exposure indicates the photosensitizer's higher efficacy. This study investigated the antimicrobial activity of metal-free (1) and indium(III) porphyrin (2) conjugates with titanium dioxide nanoparticles synthesized from orange-peel extract (TP) and orange juice (TJ).

The bacterial suspensions in PBS without any photosensitizer were used as controls. The photosensitizers showed negligible dark toxicity (Fig. S5) at concentration from (0.05–1.00 mg mL−1). Concentration optimization under light revealed 0.25 mg mL−1 as optimal as lower and higher concentrations showed lower efficiency. This fixed concentration was used for systematic time-dependent comparison studies (Fig. 12 and Table 4).


image file: d6ra00069j-f12.tif
Fig. 12 aPDI results studies using TP, 1, 2, 1-TP, 2-TP (a) and TJ, 1, 2, 1-TJ, 2-TJ (b) against S. aureus in PBS suspension. The experiments were conducted for 30 minutes with 5 minutes sampling intervals under light and control experiments were done using the bacteria only, without any photosensitizer.
Table 4 Survival percentages of freely suspended S. aureus after photoinactivation using TP, 1, 2, 1-TP, 2-TP, TJ, 1-TJ, and 2-TJ. The experiments were conducted for 30 minutes with 5 minutes sampling intervals under light and control experiments were done using the bacteria only, without any photosensitizer
Time (min) TP 1 2 1-TP 2-TP Control TJ 1-TJ 2-TJ
0 97.9 ± 1.95 98.0 ± 1.93 99.1 ± 1.96 99.1 ± 1.94 98.2 ± 1.90 99.2 ± 3.21 97.9 ± 3.78 98.9 ± 3.66 98.8 ± 2.84
5 63.2 ± 2.42 70.23 ± 2.48 83.4 ± 2.44 70.9 ± 2.50 49.1 ± 2.84 99.1 ± 2.76 63 ± 3.98 63.6 ± 1.93 55.4 ± 2.00
10 51.9 ± 3.38 60.22 ± 3.27 71.99 ± 3.39 52.7 ± 3.28 16.2 ± 3.26 98.7 ± 1.98 55.5 ± 2.56 50.6 ± 2.90 40.3 ± 2.53
15 31.1 ± 2.21 55.5 ± 2.13 50.9 ± 2.23 20.6 ± 2.15 0.022 ± 0.04 98.5 ± 2.46 45.9 ± 3.35 35.4 ± 3.32 31.8 ± 3.41
20 20.7 ± 1.78 45.6 ± 1.75 38.4 ± 1.79 0.009 ± 0.01 0.006 ± 0.00 98.4 ± 3.41 37.8 ± 2.22 20.9 ± 2.16 18.9 ± 3.31
25 10.3 ± 3.05 39.2 ± 3.42 35.2 ± 3.06 0.003 ± 0.00 0.001 ± 0.00 98.3 ± 2.24 24.9 ± 1.18 0.07 ± 0.02 0.3 ± 0.10
30 6.2 ± 2.65 20.43 ± 2.59 20.1 ± 2.67 0.001 ± 0.00 0.0006 ± 0.00 98.1 ± 2.23 13.8 ± 1.09 0.03 ± 0.01 0.01 ± 0.00


Notably, the control alone without the photosensitizer did not cause any significant reduction in the survival percentage of the bacteria in both the dark and light experiments. However, the porphyrins 1 and 2 reduced S. aureus survival, up to approximately 20% after exposure to LED light. Notably, porphyrin 2 performed better than 1 alone as expected due to the heavy atom effect of the indium that assists in promoting intersystem crossing during the photoinactivation.51 The nanoparticles TP and TJ show comparatively better antimicrobial activity with TP performing better than TJ. The reason behind this is unclear, however, it may be due distinct phytochemical profiles, pH, sugar content, and viscosity of the extracts, affecting reduction kinetics, particle size, and surface capping.

The conjugates, 1-TP, 2-TP, 1-TJ and 2-TJ were observed to cause significant reduction of bacteria. 2-TP caused almost complete inactivation of S. aureus after just 15 min, while 2-TJ achieved this after 25 minutes. The highest reduction in the survival percentage (0.0004%) was observed with the 2-TP conjugates after 30 minutes indicating a strong interaction between the indium metalated porphyrin and the nanoparticles. This superiority directly correlates with 2-TP's optimized photophysical parameters, where both heavy atom effect quenching and porphyrin electron transfer to TiO2 maximizes triplet population and singlet oxygen production.15

The results suggest that the survival percentage is inversely proportional to the irradiation time. Moreover, conjugation with TiO2 increases the antibacterial activity.

3.9.4 aPDI results for antibiofilm studies using free photosensitizers. Biofilms are complex communities of bacteria enclosed in a protective matrix, making them resistant to antimicrobial treatments. For this reason, a higher photosensitizer concentration (0.50 mg mL−1) than that used in the planktonic bacteria was found to be optimal (Fig. S5). The results in Fig. 13 and Table 5 showed that the porphyrins significantly inhibited biofilm growth, with survival percentages as low as 49.1% and 40.1% for 1 and 2, respectively. These values are better than what has been previously reported with porphyrins such as TAPP and TCPP which inhibited S. aureus biofilms by 37% and 48%.52 Notably, S. aureus, with its single membrane layer, is known to be comparably susceptible to the antibacterial effects. The porphyrins likely inhibit bacterial cell metabolism, damage the cytoplasmic membrane, and increase cell permeability.28
image file: d6ra00069j-f13.tif
Fig. 13 aPDI results studies using TP, 1, 2, 1-TP, 2-TP (a) and TJ, 1, 2, 1-TJ, 2-TJ (b) against biofilm S. aureus. The experiments were conducted for 30 minutes with 5 minutes sampling intervals under light and control experiments were done using the biofilm bacteria only, without any photosensitizer.
Table 5 Survival percentages of biofilm S. aureus after photoinactivation using TP, 1, 2, 1-TP, 2-TP, TJ, 1-TJ, and 2-TJ. The experiments were conducted for 30 minutes with 5 minutes sampling intervals under light and control experiments were done using the biofilm S. aureus only, without any photosensitizer
Time (min) TP 1 2 1-TP 2-TP Control TJ 1-TJ 2-TJ Control
0 98.3 ± 2.28 98.0 ± 2.70 99.4 ± 3.16 99.0 ± 2.61 99.5 ± 2.61 99.2 ± 3.17 99.0 ± 2.18 98.2 ± 1.89 99.2 ± 1.86 99.9 ± 1.95
5 70.3 ± 3.82 98.3 ± 2.53 80.2 ± 2.69 66.9 ± 2.87 61.9 ± 2.42 99.1 ± 2.82 70.1 ± 3.26 75.5 ± 2.54 71.9 ± 2.81 99.4 ± 2.41
10 63.9 ± 2.65 89.3 ± 2.87 74.9 ± 3.50 41.4 ± 2.44 26.97 ± 2.93 98.7 ± 2.00 53.8 ± 2.85 61.1 ± 3.08 50.2 ± 3.23 99.2 ± 3.29
15 50.3 ± 1.40 71.4 ± 2.45 63.3 ± 2.27 30.9 ± 2.15 10 ± 3.20 98.5 ± 2.60 47.9 ± 1.64 49.3 ± 2.25 56.9 ± 2.06 98.7 ± 2.13
20 35.8 ± 2.92 60.6 ± 2.23 58.8 ± 2.94 26.1 ± 2.98 0.32 ± 0.05 98.4 ± 3.38 39.2 ± 2.47 34.2 ± 1.71 29.3 ± 1.59 98.4 ± 1.74
25 22.07 ± 3.17 55.2 ± 2.99 45.7 ± 3.19 13.4 ± 2.28 0.02 ± 0.00 98.3 ± 2.27 28.2 ± 3.13 20.5 ± 3.35 15.2 ± 3.19 98.3 ± 3.46
30 12.6 ± 2.70 49.1 ± 2.70 40.1 ± 2.73 3 ± 0.83 0.004 ± 0.00 98.2 ± 1.85 20.1 ± 2.71 12.9 ± 2.49 10.4 ± 2.16 98.1 ± 2.62


Biofilms are known to be difficult to inactivate as the ROS first needs to pass through the EPS matrix to rich the target bacteria. This explains the slightly reduced efficiency of the photosensitizers against biofilms as compared to the bacteria in their freely forms. Nevertheless, the results demonstrated that the conjugates derived from TP exhibited higher efficiency in eradicating biofilms compared to those synthesized from TJ, complementing the results from freely suspended bacteria. Further investigation is needed to elucidate the specific mechanisms underlying the enhanced antibiofilm activity of TP conjugates. The best performing photosensitizer, 2-TP, achieved almost complete reduction of biofilm S. aureus after 20 min, which is longer than what was achieved using the same photosensitizer to inactivate freely suspended bacteria, which required only 15 minutes to achieve the same effect.

3.9.5 Photoinactivation of freely suspended bacteria using immobilized photosensitizers. The synthesized 1 and 2, TiO2 nanoparticles, as well as their corresponding conjugates immobilized onto waste PS were tested for photodynamic activity. PS support allows for ease of separation of the photosensitizer after use. The test microorganism was still the same, environmental S. aureus, in both suspension and biofilm. Control experiments with the bacterial suspension but without a photosensitizer, and with the photosensitizers in the dark, showed essentially no significant photodynamic effect.

PS is a polymer that has been found not to cause inhibition against S. aureus.23 Hence, in this study, PS alone (Table 6) showed no significant change in the survival percentage of the bacteria. The trend in the efficiency of the photosensitizers is almost the same in their free, as well as immobilized forms. Notably, the photosensitizers immobilized onto PS were found to have a slightly reduced antimicrobial activity compared to the photosensitizers in their free forms as expected. For example, only 2-TP could cause significant bacterial reduction, achieving almost complete (0.01%) reduction in the survival percentage after 25 minutes. Notably, this was even longer than inactivation of freely suspended bacteria using free 2-TP (almost complete survival percentage reduction after 15 minutes).

Table 6 Survival percentages of freely suspended S. aureus after photoinactivation using PS immobilized photosensitizers TP-PS, 1-PS, 2-PS, 1-TP-PS, 2-TP-PS, TJ-PS, 1-TJ-PS, and 2-TJ-PS. The experiments were conducted for 30 minutes with 5 minutes sampling intervals under light and control experiments were done using the bacteria only, without any photosensitizer
Time (min) TP-PS 1-PS 2-PS 1-TP-PS 2-TP-PS Control TJ-PS 1-TJ-PS 2-TJ-PS PS Control
0 99.9 ± 3.12 99.3 ± 3.00 99.6 ± 3.27 99.3 ± 3.65 99.0 ± 3.67 99.4 ± 3.69 99.7 ± 3.01 99.8 ± 1.87 99.8 ± 2.25 98.1 ± 3.33 98.9 ± 2.86
5 79.3 ± 2.67 98.9 ± 3.04 89.3 ± 2.23 74.6 ± 2.05 99.2 ± 2.83 99.4 ± 2.78 70.8 ± 2.34 69.3 ± 2.86 60.3 ± 2.09 97.8 ± 4.64 98.5 ± 2.75
10 76.1 ± 2.32 90.2 ± 4.21 82.9 ± 2.01 53.8 ± 2.77 32.3 ± 3.29 99.3 ± 3.33 66.9 ± 3.35 51.9 ± 3.12 49.1 ± 3.10 97.7 ± 2.74 98.3 ± 3.54
15 59.9 ± 2.34 83.3 ± 2.39 74.1 ± 2.96 36.9 ± 2.96 21.4 ± 2.01 99.1 ± 3.23 64.6 ± 3.82 43.5 ± 2.22 38.9 ± 2.00 97.5 ± 3.63 98.2 ± 2.55
20 41.5 ± 3.00 72.7 ± 2.88 62.9 ± 3.47 24.1 ± 3.05 4.9 ± 1.21 98.9 ± 3.76 52.8 ± 1.66 31.3 ± 3.54 24.8 ± 3.50 97.33 ± 2.43 98.2 ± 1.87
25 31.7 ± 2.23 60.8 ± 1.67 56.8 ± 1.37 17.5 ± 1.32 0.01 ± 0.01 98.5 ± 2.26 43.3 ± 1.56 20.9 ± 2.77 8.2 ± 0.90 97.1 ± 3.44 97.8 ± 1.34
30 29.8 ± 1.97 58.2 ± 2.98 51.1 ± 2.14 9.3 ± 1.19 0.006 ± 0.00 98.5 ± 2.45 31.9 ± 1.06 7.9 ± 1.11 0.04 ± 0.01 96.1 ± 1.34 97.6 ± 2.86


3.9.6 Photoinactivation of biofilm bacteria using immobilized photosensitizers. The photoinactivation of biofilm bacteria using immobilized photosensitizers was also investigated, with the goal of developing a more practical and reusable antimicrobial system. The results in Table 7 showed that the immobilized photosensitizers, including 1, 2, TP, TJ, and their conjugates, exhibited slightly reduced antibiofilm activity compared to their free forms. However, the 2-TP conjugate immobilized on PS still achieved significant biofilm reduction, with almost complete (0.9%) inactivation of S. aureus biofilm after 30 minutes of light exposure. The conjugates from TJ could not cause almost complete reduction in bacterial survival percentage. However, 2-TJ showed better efficiency, achieving 4.4% survival percentage after 30 minutes of light exposure.
Table 7 Survival percentages of biofilm S. aureus after photoinactivation using PS immobilized photosensitizers TP-PS, 1-PS, 2-PS, 1-TP-PS, 2-TP-PS, TJ-PS, 1-TJ-PS, and 2-TJ-PS. The experiments were conducted for 30 minutes with 5 minutes sampling intervals under light and control experiments were done using biofilm S. aureus only, without any photosensitizer
Time (min) TP-PS 1-PS 2-PS 1-TP-PS 2-TP-PS Control TJ-PS 1-TJ-PS 2-TJ-PS PS Control
0 99.4 ± 3.39 98.6 ± 3.54 99.2 ± 3.46 99.3 ± 3.95 99.8 ± 3.33 99.6 ± 3.97 99.5 ± 3.34 99.9 ± 2.29 98.9 ± 3.42 99.8 ± 3.21 99.9 ± 3.17
5 86.9 ± 3.41 98.2 ± 2.89 93.3 ± 3.68 78.4 ± 2.65 71.1 ± 2.87 99.4 ± 3.20 90.2 ± 1.18 82.5 ± 1.87 74.9 ± 3.33 98.5 ± 3.12 99.8 ± 2.82
10 76.3 ± 2.90 94.3 ± 2.05 83.1 ± 2.65 64.7 ± 3.33 58.3 ± 1.98 99.2 ± 2.09 78.3 ± 1.99 68.4 ± 1.68 61.2 ± 2.58 98.2 ± 4.00 99.6 ± 2.00
15 50.3 ± 2.06 80.5 ± 3.00 76.9 ± 2.51 54.4 ± 3.19 39.5 ± 1.76 98.7 ± 2.99 67.4 ± 2.76 56.6 ± 1.44 46.9 ± 2.95 97.9 ± 3.60 99.5 ± 2.60
20 45.8 ± 1.32 69.4 ± 1.03 63.7 ± 2.55 38.8 ± 2.64 20.9 ± 1.20 98.2 ± 1.00 52.3 ± 2.37 38.9 ± 1.34 30.0 ± 3.19 97.6 ± 3.26 99.5 ± 3.38
25 39.9 ± 2.48 54.3 ± 2.28 49.1 ± 3.65 15.5 ± 1.39 3.4 ± 1.32 97.8 ± 1.68 46.5 ± 2.87 25.3 ± 1.11 21.9 ± 3.27 97.4 ± 3.81 99.5 ± 2.27
30 32.8 ± 3.49 50.4 ± 2.88 43.7 ± 2.45 2.5 ± 1.17 0.9 ± 0.04 97.5 ± 3.87 39.1 ± 2.82 10.4 ± 1.79 4.4 ± 2.70 97.3 ± 1.74 99.2 ± 1.85


This demonstrates the potential of immobilized photosensitizers for practical applications, such as coating water storage systems surfaces to prevent biofilm formation and reduce the risk of waterborne infections. While the level of antimicrobial photodynamic activity observed is not yet sufficient for practical purposes, where a 5-log kill would be desirable, with this model system, the study has demonstrated the concept that the photodynamic effect with immobilized photosensitizers can be used to lower microbial levels in water. The system might also have applications to water decontamination.

4 Conclusions

Metal-free (1) and indium metalated (2) 5,10,15-tris-(4-bromopheyl)-20-(4-carboxyphenyl)porphyrin conjugates with green synthesized TiO2 nanoparticles were synthesized successfully and immobilized onto waste PS. Their photophysical behaviour was evaluated which showed that conjugates generate higher amount of singlet oxygen, thus, better photosensitizers compared to the porphyrins (1 and 2) alone and an indication that introduction of TiO2 into the porphyrin improves the efficiency of porphyrin complexes as photosensitizers. Furthermore, the conjugates with TiO2 synthesized from orange peel extract performed better than those from orange juice indicating that the different phytochemicals within the materials play a significant role in their efficiency. Antimicrobial studies revealed significant efficiency of the conjugates in their free and immobilized forms against freely suspended and biofilm S. aureus under light. The study demonstrated that porphyrin conjugates from green synthesized TiO2 may have potential to be used for inactivation of biofilms in water storage systems via antimicrobial photodynamic inactivation.

Author contributions

N. M.: conceptualization, visualization, methodology, formal analysis, investigation, and writing—original draft. N. K. M.: methodology, investigation, writing. C. I. N.: writing – review, funding acquisition and editing. O. J. A. writing – review, funding acquisition and editing. R. M. M.: validation, project administration, writing—review and editing, supervision. M. M.: conceptualization, validation, resources, funding acquisition, project administration, writing—review and editing, supervision. All authors have read and agreed to the published version of the manuscript.

Conflicts of interest

There are no conflicts to declare.

Data availability

The data supporting this article has been included as part of the supplementary information (SI). The raw/processed data required to reproduce these findings cannot be shared at this time as the data also form part of an ongoing study. Supplementary information is available. See DOI: https://doi.org/10.1039/d6ra00069j.

Acknowledgements

This research was funded by the Royal Society through grant number ICAO/R1/231012 – International Science Partnership Fund (ISPF) – International Collaboration Awards and Institute for Nanotechnology and Water Sustainability (iNanoWS), University of South Africa (UNISA). This work was supported by the University of South Africa, Institute for Nanotechnology and Water Sustainability (iNanoWS), CSIR National Laser Centre, as well as the Department of Science, Innovation and Technology (DSTI), South Africa through the South African Women in Science Awards (SAWiSA) DSTI-Esther Mahlangu Fellowship (Masters).

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