Contaminant-activated visible light photocatalysis

ABSTRACT Pristine titanium dioxide (TiO2) absorbs ultraviolet light and reflects the entire visible spectrum. This optical response of TiO2 has found widespread application as white pigments

in paper, paints, pharmaceuticals, foods and plastic industries; and as a UV absorber in cosmetics and photocatalysis. However, pristine TiO2 is considered to be inert under visible light

for these applications. Here we show for the first time that a bacterial contaminant (_Staphylococcus aureus—_a MRSA surrogate) in contact with TiO2 activates its own photocatalytic

degradation under visible light. The present study delineates the critical role of visible light absorption by contaminants and electronic interactions with anatase in photocatalytic

degradation using two azo dyes (Mordant Orange and Procion Red) that are highly stable because of their aromaticity. An auxiliary light harvester, polyhydroxy fullerenes, was successfully

used to accelerate photocatalytic degradation of contaminants. We designed a contaminant-activated, transparent, photocatalytic coating for common indoor surfaces and conducted a 12-month

study that proved the efficacy of the coating in killing bacteria and holding bacterial concentrations generally below the benign threshold. Data collected in parallel with this study showed

a substantial reduction in the incidence of infections. SIMILAR CONTENT BEING VIEWED BY OTHERS IMPACT OF SURFACE TOPOGRAPHY AND HYDROPHOBICITY IN VARIED PRECURSOR CONCENTRATIONS OF TENORITE

(CUO) FILMS: A STUDY OF FILM PROPERTIES AND PHOTOCATALYTIC EFFICIENCY Article Open access 04 April 2024 VISIBLE LIGHT-INDUCED PHOTOCATALYTIC AND ANTIBACTERIAL ADHESION PROPERTIES OF

SUPERHYDROPHILIC TIO2 NANOPARTICLES Article Open access 04 April 2024 FABRICATION AND EVALUATION OF DURABLE, OPTICALLY CLEAR, AND SELF-DISINFECTING FILMS Article 15 July 2021 INTRODUCTION

Patients and visitors in healthcare facilities can acquire infections by direct or indirect contact with common surfaces (room door handles, bed rails, taps, sterile packaging, mops, ward

fabrics and plastics, keyboards and telephones) that have become contaminated with pathogenic microbes1. Making these surfaces microbe-unfriendly can break the cycle of contamination and

infection. Antimicrobial coatings that slowly release toxic silver or copper ions, currently in clinical trials2,3,4,5, have limited lifetime, are difficult to apply and are costly6,7,8,9.

Further, copper surfaces were unable to reduce bacterial concentrations to the benign level in clinical trials2,4. TiO2 photocatalysis has attracted intense interest for applications in

self-cleaning and antimicrobial coatings as TiO2 can completely mineralize organic contaminants including microorganisms and the process produces no toxic by-products10,11,12. Further, TiO2

is environmentally benign and inexpensive13,14. Unfortunately, TiO2, which is an excellent photocatalyst under UV light, has very limited capability for visible light absorption11,15,16.

Extension of TiO2 photocatalysis to visible light is a highly active area of research17,18,19,20,21,22,23,24. Major approaches are: _1)_ creation of defects within the TiO2 crystalline

structure, such as oxygen or titanium vacancies or substitutions. Techniques include doping (with elements such as, carbon, nitrogen, sulfur or phosphorous), annealing in reducing

atmospheres and synthesis in the presence of reductants24,25,26,27; _2)_ creation of defects at the TiO2 surface. Techniques include surface hydrogenation, plasma treatment and surface

amination26,28,29; _3)_ combination of visible light harvesters with the TiO2. Techniques include co-synthesis with materials such as gold, copper and quantum dots24,30,31, and mixing with

organic dyes, such as methylene blue, porphyrin and metal-quinoline complexes24,32,33,34. The three methods differ with respect to the site of visible light absorption and concomitant

exciton generation: throughout the modified crystal, at the surface of the modified crystal or in the light harvester. With respect to the third method, exciton-exciton annihilation within

light harvesters is suppressed by transfer of excited electrons to TiO2, which has high electron affinity15. Among the techniques for extending the TiO2 photocatalysis in visible region,

mixing with organic dyes is by far the simplest and is the basis for dye-sensitized solar cells35. Unfortunately, the dyes are photocatalytically degraded, leading to a short-term benefit24.

In this report, we show that model organic contaminants (two organic dyes, Mordant Orange and Procion Red, and the bacterium, _Staphylococcus aureus_) in contact with pristine TiO2

(anatase) can harvest visible light and transfer electrons to TiO2, resulting in photocatalytic degradation of the contaminants. We also show, for the first time, that a natural, bacterial

contaminant (_S. aureus_) with very low levels of light absorption is inactivated on pristine TiO2 by the same mechanism. In this mechanism, which we refer to as contaminant activated

photocatalysis, the rate of photocatalytic degradation depends on the extent of visible light absorption. This new information is utilized to design transparent, contaminant activated

photocatalytic coatings for prevention of healthcare-acquired infections. RESULTS AND DISCUSSION CHARACTERIZATION OF ANATASE TIO2 The X-ray diffraction pattern for TiO2 (Fig. 1a) has

characteristic peaks at 25.4°, 37.8°, 48.0°, 53.7°, 54.9°, 62.8° and 75.1° that are assigned to (101), (004), (200), (105), (211), (204) and (215) crystal planes of anatase. The crystallite

size of TiO2 was estimated from the Scherrer equation to be 7 nm. The X-ray photoelectron spectroscopic (XPS) analysis of TiO2 (Fig. 1b) indicated the presence of titanium, oxygen and

adventitious carbon. The band gap was determined to be 3.2 eV from ground-state absorption spectrum (Fig. 1c) using UV-Vis spectrophotometer with integrating sphere and the valence band

maximum energy was determined to be 2.05 eV from valence band spectrum (Fig. 1d) using XPS. These values are consistent with reported values24,25,27,36. The Ti 2p spectrum (Fig. 1e) exhibits

the Ti 2p3/2 peak at 458.1 eV and Ti 2p1/2 peak at 463.8 eV, which are consistent with reported Ti4+ values25,26. No Ti3+ peaks were present. The O 1 s spectrum (Fig. 1f) has peaks at 529.3

 eV, 530.5 eV and 531.7 eV that are attributed to oxygen in TiO2 lattice, surface Ti-OH and physisorbed water, respectively26,37. The binding energy differences between core emission lines

and the valence band maxima Δ_E_Ti-VB = 456.05 eV and Δ_E_O-VB = 527.25 eV are consistent with the reported values for anatase36. ELECTRONIC INTERACTIONS BETWEEN CONTAMINANTS AND TIO2 To

test our hypothesis that contaminant mediated absorption of visible light activates TiO2 photocatalysis, we chose two model contaminants that absorb visible light at different

wavelengths—mordant orange with peak absorption at 374 nm (Fig. 2a) and procion red with peak absorption at 518 nm (Fig. 2b). Tiles were coated with TiO2 and the contaminants were pipetted

onto the coated tiles, allowed to spread and dried in the dark (see supplementary information). Absorption spectra for the model contaminants in contact with TiO2 (MO@TiO2 and PR@TiO2) are

shown in Fig. 2a,b, respectively. For comparison, the absorption spectra for model contaminants in contact with silica coatings (MO and PR) are also shown. Absorption peaks of the model

contaminants on silica coating are the same as the peaks obtained for the contaminants in aqueous solution, suggesting that there was no interaction between either mordant orange or procion

red and silica. Adsorption of contaminants onto the TiO2 coated surfaces cause bathochromic (red) shift and broadening of the light absorption peaks and shifting of the absorption edges to

lower energies. These changes to light absorption suggest electron transfer from model organic contaminants to TiO2 and are consistent with observations reported for dye adsorption on

TiO232. The peak and absorption edge for mordant orange are red-shifted by 38 nm and 0.24 eV, respectively, and the peak and absorption edge for procion red are red-shifted by 4 nm and 0.02 

eV, respectively. The greater red-shift for mordant orange suggests stronger electronic interaction with TiO2. As shown in Fig. 2c,d, the valence band maxima for TiO2 in contact with the

contaminants exhibit both a shift to lower energies and addition of a tail, similar to observations for anatase synthesized with dopants or defects25,27,28,38. The valence band maximum for

mordant orange + TiO2 is 1.8 eV with a tail at 1.3 eV, whereas the valence band maximum for procion red + TiO2 is 2.05 eV with a tail at 1.6 eV. The greater shift in valence band maximum for

mordant orange + TiO2 is consistent with the greater bathochromic shift and suggests stronger electronic interactions. The Ti 2p spectra are not appreciably changed by addition of model

contaminants to the TiO2 (Fig. 2e,f). However, a strong secondary peak is observed in the O 1 s spectra, corresponding to oxygen in the model contaminants (Fig. 2g,h). These results indicate

that contacting model contaminant with pristine TiO2 effects changes in electronic properties of photocatalyst similar to those obtained by doping TiO2 with elements such as carbon or

nitrogen24; co-synthesizing TiO2 with light harvesters such as phosphorous or quantum dots25; or surface modifying TiO2 by, for example, surface hydrogenation28. CONFIRMATION OF MECHANISM OF

CONTAMINANT ACTIVATED PHOTOCATALYSIS The hypothetical mechanism of contaminant activated visible light photocatalysis is shown in Fig. 3a. Visible light is absorbed by the contaminant,

generating electron-hole pairs (excitons). Excited electrons are scavenged from the contaminant by anatase, which has high electron affinity15. These electrons react with oxygen and water at

the surface of TiO2 particles forming highly labile oxygen species, such as superoxide radicals and hydroxyl radicals (ROS) that, in turn, decompose the contaminant. If this mechanism is

correct, contaminant degradation should depend on overlap between the contaminant’s absorption spectrum and the incident light spectrum. To confirm this dependency, we used optical longpass

filters to, in effect, create several wavelength bands in the region between 385 nm (the lower limit of emission of the fluorescent lamps employed experimentally) and 800 nm (nominally the

upper limit of visible light). Experiments were carried out under room light produced by fluorescent lamps, which emit light with wavelength greater than 385 nm (see Figure S1 for spectral

distribution of the lamp). According to our hypothesis, mordant orange, which absorbs most strongly at 400 nm, should be degraded fastest with light in this wavelength region. This was

confirmed experimentally (Fig. 3b). Relative contribution of wavelength bands to the overall degradation rate are shown in bottom graph of Fig. 3b. The wavelength bands evaluated were

determined by the lower bound of emission (385 nm) from the fluorescent lamps used for illumination and the cutoff wavelengths (400, 495, 550 nm) of the longpass optical filters employed.

The wavelength band of 400 to 495 nm contributed to 64% of overall degradation rate (0.018 hr−1). Similarly, procion red, with an absorption peak at 520 nm, was degraded most rapidly within

the wavelength band of 495 to 550 nm (Fig. 3c). Controls consisting of dye on a photocatalytically inert surface (silica) and dye on TiO2 in darkness showed effectively no activity,

indicating that both TiO2 and visible light are required for photocatalytic degradation. The optical filters introduced a slight decrease in overall light intensity with increasing cutoff

wavelength, but a modest decrease on this same order was shown to have negligible effect on photocatalytic degradation rate (Figure S2). Thus, it is seen that the rate of photocatalysis

under visible light correlates strongly with light absorption by organic contaminants. An auxiliary visible light harvester should be able to enhance photocatalytic degradation through

increased exciton generation and, concomitantly, electron transport to TiO2 where ROS are formed (Fig. 4a). Polyhydroxy fullerenes (PHF), because of its broadband absorption (Fig. 4b) and

high degree of stability39,40, should be an excellent candidate for this role. As shown in Fig. 4c, incorporation of PHF in the TiO2 coating increased the contaminant degradation rate by up

to 2.5 times, depending on wavelength. The largest effect was observed with light between 400 nm and 495 nm. Cutoff beyond 550 nm led to very low rates with or without PHF. COATING

OPTIMIZATION Coating formulation was optimized to obtain a transparent and uniform photocatalytic coating as well as a stable formulation. Transparent photocatalytic coatings were obtained

with a particle loading equal to 128 µg/cm2, giving a nominal thickness of 0.25 µm (Fig. 5a)10. Surfactants were investigated to disperse the formulation, but were found to inhibit

contaminant activated photocatalysis (Fig. 5b). Electrostatic dispersion with NaOH (pH 9–10) provided a stable formulation (Figure S3) without compromising photocatalytic activity (Fig. 5b).

In the absence of dispersant, the coating consisted of 10–100 µm agglomerates (Fig. 5c), whereas the agglomerate size in the electrostatically dispersed coating was less than 1 µm (Fig. 

5d). A commercial rutile phase of TiO2 with mean crystallite size of 22 nm was investigated as a bottom coating because of its observed tendency to form dense, uniform layer on ceramic tile.

A dual phase coating prepared by applying a layer of rutile followed by a layer of anatase was compared to a two-layer coating consisting solely of anatase. The dual phase (rutile/anatase)

coating performed slightly better than anatase (anatase/anatase) coating and was therefore adopted for the bacterial inactivation experiments (Figure S4). ACTIVATION OF VISIBLE LIGHT

PHOTOCATALYSIS BY MRSA SURROGATE A benign strain of the bacterium, _Staphylococcus aureus_ (ATCC 25923), was chosen as a surrogate for MRSA. As shown in Fig. 6a, _S. aureus_ is a very weak

absorber of blue light (absorption peak at 411 nm; 0.0256 absorbance at 108 CFU/cm2; absorption edge at 2.31 eV). Thus, it provided a severe test of the ability of a microbial contaminant to

activate TiO2 photocatalysis under visible light. Dual phase (rutile bottom layer/ anatase top layer) TiO2 coating was prepared on tiles and 0.1 mL of _S. aureus_ suspension (2–3 × 105 

CFU/mL) was pipetted onto each coated tile surface and allowed to spread, giving a surface loading of ~8000 CFU/cm2. One set of tiles with photocatalytically inert silica substituted for the

anatase top layer was also prepared. The tiles were dried in the dark in a biosafety cabinet for 3 hours (see supplementary methods). As shown in Fig. 6b, control (dark) experiments with

_S. aureus_ on TiO2 coated tiles had inactivation rate of 0.031 ± 0.002 hr−1, which is attributable to desiccation. The rutile/silica coating under visible light inactivated _S. aureus_ at a

rate of 0.072 ± 0.02 hr−1, which is significantly greater (α = 0.001) than the dark control. Since rutile absorbs visible light up to a wavelength of 409 nm, the observed inactivation could

be independent of light harvesting by _S. aureus_. However, in the rutile/anatase coating, the _S. aureus_ inactivation rate was significantly (α = 0.001) increased to 0.103 ± 0.01 hr−1,

providing confirmation of contaminant activated photocatalysis. Addition of auxiliary light harvester (PHF) increased the bacterial inactivation rate by up to 1.55 times (0.161 ± 0.01 hr−1

for rutile/anatase + 0.1 PHF). Photocatalysis inactivates cells by degrading the cell surface. The _S. aureus_ used in the present study expresses a capsule, which protects the cell-surface.

Most MRSA strains do not express a capsule41, and therefore should be more susceptible to contaminant activated photocatalysis. TESTING OF OPTIMIZED COATING IN A BETA FACILITY The optimized

antimicrobial coating was further evaluated for its ability to control the microbial burden on surfaces in a beta facility. A commercial primer (BioShield NuTiO) replaced the bottom rutile

layer in the optimized coating to provide a binding agent for the top antimicrobial layer. Surfaces (walls, counters, door knobs, lockers, thermostat, bed rail, bathroom rail and soap

dispensers) were initially steamed to ensure primer adhesion, allowed to dry for 15 minutes, coated with primer, and allowed to dry for another 15 minutes. The top antimicrobial layer was

then applied using commercial foggers. Selected surfaces were tested for bacterial count a total of five times: initially 1 hour after application of the antimicrobial coating, and

subsequently 2, 4, 6 and 12 months after initial application of the coating. The bacterial counts over this 12-month period for each surface are shown in Fig. 7. The different surfaces are

arranged along the x-axis of the figure, whereas the temporal variation of bacterial counts on each surface is indicated by a sequence of five bars, one for each time of sampling. The wall

(W) and thermostat (T) had initial bacterial counts below the benign limit of 2.5 CFU/cm2 (64 CFU/ 4 sq.in.) proposed by Griffith _et al_.2,42. No significant change in bacterial count over

the total 12 month period was observed on the wall, whereas the count on the thermostat decreased by 93% within 2 months. Initial bacterial counts on both lockers (L) and door knobs (K)

greatly exceeded the benign limit. Counts on these surfaces decreased by 99% within 2 months and remained within the benign range for rest of the study. Soap dispensers (D) had low counts

(within benign limit), possibly due to antimicrobial agents used in the soap. Initial bacterial counts on bathroom rails (R) and bed rails (B) were above the benign limit, with bed rails

exhibiting the highest initial counts among all surfaces studied. Bacterial counts on the bathroom rails and bed rails decreased significantly throughout the study. Bacterial levels on the

kitchen counter (C) were very high initially and remained above the benign limit for all but the last sampling. Of the five surfaces with initial bacterial counts above the benign level,

only the kitchen counter failed to exhibit a consistent reduction in bacterial level. This could be due to frequent wiping (several times daily), which could have removed the antimicrobial

coating. The incidence of acquired infections in the beta facility during the first six months of the study was reduced by 55% compared to the previous year. The beta facility results

suggest that contaminant-activated photocatalysis can transform common indoor surfaces into antimicrobial surfaces with potential to break the cycle of contamination and infection.

CONCLUSIONS We have demonstrated for the first time that bacteria can sensitize pristine TiO2 to visible light, resulting in photocatalytic inactivation of the bacteria. Specific conclusions

are as follow: * Contacting pristine anatase with a visible-light-absorbing model contaminant creates, in effect, a photocatalyst with smaller bandgap and lower valence band maximum than

the anatase. * The degradation rate of model contaminants in contact with pristine anatase is strongly correlated with visible light absorption by the contaminants. * _Staphylococcus aureus_

with very weak visible light absorption was successfully inactivated on transparent, pristine TiO2 coatings. * Bacteria that do not express a capsule, as well as viruses, should be at least

as susceptible to contaminant activated photocatalysis as the test strain of _S. aureus_. * Incorporation of an auxiliary light harvester (polyhydroxy fullerenes) accelerated degradation of

model contaminants by up to 2.5 times and _S. aureus_ by up to 1.5 times. * Transparent photocatalytic coatings were obtained with a particle loading of 128 µg/cm2 (0.25 µm thickness). *

Electrostatic dispersion with NaOH (pH 9–10) provides a stable formulation without compromising photocatalytic activity. * Application of photocatalytic coating to indoor surfaces decreased

bacterial counts consistently to benign levels on five of six surfaces monitored over a period of 12 months. (Bacterial counts on two other surfaces were in the benign range at the outset of

the study.) Whether organic degradation is desired or undesirable, the potential of pristine TiO2 (particularly the anatase polymorph) to photocatalytically decompose organic materials

under visible light must be taken into account in design of paints, pharmaceuticals, food additives, polymer composites, catalysts and antimicrobial coatings. METHODS Photocatalytic coating

formulation was prepared by adding 10 mg of anatase to 10 mL of dilute NaOH (pH = 9.5) in a 20 mL scintillation vial wrapped with aluminum foil to prevent exposure to visible light. The

suspension was sonicated for 30 minutes total. Rutile coating formulation and silica coating formulations were prepared in the same fashion. To prepare the anatase + PHF coating formulation,

10 mg of anatase was added to 9 mL of dilute NaOH (pH = 9.5) in a 20 mL scintillation vial wrapped with aluminum foil and the suspension was sonicated for 30 minutes. This suspension was

then amended with 1 mL of solution containing either 0.1 or 1 mg of PHF and mixed with a magnetic stirrer for 10 minutes in dark. The two formulation with PHF are referred to as TiO2 + 0.01 

PHF and TiO2 + 0.1 PHF, respectively. Coating formulations were applied to tiles within 1 hour of the preparation. Ceramic tiles were utilized to evaluate the photocatalytic degradation of

organic dye and inactivation of microbes. A volume of 0.4 mL of selected coating formulation was pipetted on the tile surface as the first coat. The coated surfaces were dried for one hour

at 40 °C in dark. A second coat of same or different coating formulation was applied following the same procedure as described above. A total surface loading of 128 μg/cm2 was achieved with

this procedure. Organic dye or _S. aureus_ suspension was applied to the test surfaces. In case of organic dye, 0.02 mL of PR solution (2000 mg/L) or MO solution (2000 mg/L) was pipetted

onto coated tiles and allowed to spread. The ratio of contaminants MO and PR was 1 µg contaminant per 10 µg of TiO2 or SiO2. The dye-coated tiles were dried at 50 °C for 20 minutes in dark

before starting the performance evaluation. In case of _S. aureus_, 0.1 mL of _S. aureus_ suspension (2–3 × 105 CFU/mL) was pipetted onto each coated tile surface and allowed to spread,

giving a surface loading of 6400–9600 CFU/cm2. The ratio of bacteria was ~80 CFU per 1 µg of TiO2. The tiles with _S. aureus_ were dried in the dark in a biosafety cabinet for 3 hours. The

photocatalytic experiments were carried out under fluorescent lamps at visible light irradiance of 1.8–2.0 W/m2. The UVA irradiance (0.000 W/m2) was below the detection limit of the

instrument consistent with no UV emission from the fluorescent lamp spectra. The temporal changes in dye concentration were determined by measuring the absorbance after predetermined times

of exposure to visible light. The inactivation of _S. aureus_ was evaluated by determining the viable counts after exposure to visible light. The significance of visible light absorption by 

model contaminants was delineated by employing filters to limit the wavelengths of visible light available for absorption. Four 400 nm longpass filters (2″ × 2″) were joined to form a square

of 4″ × 4″ held together by transparent tape. The coated tiles with PR or MO dyes were prepared as mentioned previously. In each experiment, four tiles were placed in a Petri dish. In case

of neutral filter experiments, the Petri dishes were covered with their lids. In case of longpass filter experiments, The 4″ × 4″ filters were placed on the Petri dish (without lids) and the

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  CAS  PubMed  Google Scholar  Download references ACKNOWLEDGEMENTS The authors acknowledge the financial support from the NSF-Accelerated Innovation Research (IIP#1127830) and NSF-I/UCRC

Center for Particulate and Surfactant Systems (IIP#0749481), Center for Nano Bio Sensors and Particle Engineering Research Center. Any opinions, findings, conclusions or recommendations

expressed herein are those of the author(s) and do not necessarily reflect the views of the NSF. Partial support for W.B. was provided by a University of Florida Alumni Fellowship. SEM and

XPS were carried out at the Major Analytical Instrumentation Center by Kerry Siebein and Eric Lambers, respectively. XPS was carried out at the Swagelok Center for Surface Analysis of

Materials and was supported by Lerner Research Institute’s seed funds for V.K. All photocatalysis experiments were conducted at the UF Water Reclamation and Reuse Laboratory. AUTHOR

INFORMATION Author notes * Vijay Krishna Present address: Department of Biomedical Engineering, Lerner Research Institute, Cleveland Clinic, Cleveland, OH, 44195, USA * Wei Bai Present

address: Sinmat, Inc., Gainesville, FL, 32653, USA * Zhao Han Present address: Western Digital Corporation, San Jose, CA, 95138, USA * Akihiro Yano Present address: Mitsubishi Plastics,

Inc., Tokyo, Japan * Abhinav Thakur Present address: Freeport-McMoRan Copper & Gold Inc., Bagdad, AZ, 86321, USA * Joseph Navarro Present address: Synergy Sales Co., Sarasota, FL, 34232,

USA AUTHORS AND AFFILIATIONS * Particle Engineering Research Center, University of Florida, Gainesville, FL, 32611, USA Vijay Krishna, Wei Bai, Zhao Han, Akihiro Yano, Abhinav Thakur, 

Angelina Georgieva, Ben Koopman & Brij Moudgil * Department of Materials Science and Engineering, University of Florida, Gainesville, FL, 32611, USA Vijay Krishna, Zhao Han, Abhinav

Thakur & Brij Moudgil * Department of Environmental Engineering Sciences, University of Florida, Gainesville, FL, 32611, USA Wei Bai & Ben Koopman * Nagoya Institute of Technology,

Tajimi, Gifu, 5070033, Japan Akihiro Yano * Village on the Isle, Venice, FL, 34285, USA Kristy Tolley * NanoHygienix LLC, Sarasota, FL, 34236, USA Joseph Navarro Authors * Vijay Krishna View

author publications You can also search for this author inPubMed Google Scholar * Wei Bai View author publications You can also search for this author inPubMed Google Scholar * Zhao Han

View author publications You can also search for this author inPubMed Google Scholar * Akihiro Yano View author publications You can also search for this author inPubMed Google Scholar *

Abhinav Thakur View author publications You can also search for this author inPubMed Google Scholar * Angelina Georgieva View author publications You can also search for this author inPubMed

 Google Scholar * Kristy Tolley View author publications You can also search for this author inPubMed Google Scholar * Joseph Navarro View author publications You can also search for this

author inPubMed Google Scholar * Ben Koopman View author publications You can also search for this author inPubMed Google Scholar * Brij Moudgil View author publications You can also search

for this author inPubMed Google Scholar CONTRIBUTIONS V.K. and W.B. in collaboration with B.K. and B.M., conceived and designed the experiments, and analyzed the data. W.B. and Z.H.

performed the contaminant-activated photocatalysis experiments and data analysis. V.K., A.Y. and A. T. characterized the optical properties of the coatings and contaminants. A.G. synthesized

and characterized auxiliary light harvester. J.N., K.T. and W.B. conducted the beta facility testing with additional help from V.K. and Z.H. The manuscript was written by V.K. and B.K. with

input from W.B. and B.M. CORRESPONDING AUTHOR Correspondence to Vijay Krishna. ETHICS DECLARATIONS COMPETING INTERESTS The authors declare that they have no competing interests. ADDITIONAL

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THIS ARTICLE CITE THIS ARTICLE Krishna, V., Bai, W., Han, Z. _et al._ Contaminant-Activated Visible Light Photocatalysis. _Sci Rep_ 8, 1894 (2018). https://doi.org/10.1038/s41598-018-19972-0

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