Journal of Nanomaterials
Volume 2015 (2015), Article ID 210734, 8 pages
http://dx.doi.org/10.1155/2015/210734

Research Article

Silver Nanoparticles Influence on Photocatalytic Activity of Hybrid Materials Based on TiO₂ P25

Tomkouani Kodom,1,2 Edina Rusen,¹ Ioan Călinescu,¹ Alexandra Mocanu,¹ Raluca Şomoghi,³ Adrian Dinescu,⁴ Aurel Diacon,¹ and Cristian Boscornea¹

¹Department of Bioresources and Polymer Science, University Politehnica of Bucharest, 1-7 Gh. Polizu Street, 011061 Bucharest, Romania
²Laboratory of Water Chemistry, Faculty of Sciences, University of Lomé, Lomé, Togo
³National Research and Development Institute for Chemistry and Petrochemistry (ICECHIM), 202 Independence Street, District 6, CP 35-174, 060021 Bucharest, Romania
⁴National Institute for Research and Development in Microtechnologies (IMT-Bucharest), 126 A, Erou Iancu Nicolae Street, P.O. Box 38-160, 023573 Bucharest, Romania

Received 13 September 2014; Revised 17 December 2014; Accepted 18 December 2014

Academic Editor: Ping Xu

Copyright © 2015 Tomkouani Kodom et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

Abstract.

The aim of the present study consists in the obtaining of a hybrid material film, obtained using TiO₂ P25 and silver nanoparticles (AgNPs). The film manufacturing process involved realization of physical mixtures of TiO₂ P25 and AgNPs dispersions. The size distribution of the AgNPs proved to be a key factor determining the photodegradation activity of the materials measured using methyl orange. The best result was 33% degradation of methyl orange (MO) after 150 min. The second approach was the generation of AgNPs on the surface of TiO₂ P25. The obtained hybrid material presents photocatalytic activity of 45% MO degradation after 150 min. The developed materials were characterized by UV-VIS, SEM, and DLS analyses.

1. Introduction

One of the most omnipresent problems affecting people throughout the world is inadequate access to clean water and sanitation. Problems with water are expected to increase over the next decades, with water insufficiency occurring globally, even in regions currently assigned as water-rich [1, 2].

TiO₂ is the most commonly used oxide semiconductor in numerous fields (white pigments, dyes, and coatings, cosmetics, food, bleaching products, and solar cells) [3] which proved to be an ideal photocatalyst due to its ability to completely mineralize the target pollutants from wastewaters into H₂O and CO₂ [4]. Although TiO₂ is abundant, cost-effective, environmentally friendly, and photochemically stable under severe conditions [5], it has several disadvantages. One of these is related to the wide bandgap energy of 3.0 eV for rutile, respectively, and 3.2 eV for anatase which limits its applications, making possible the utilization of only 5% of the solar spectrum [1]. Furthermore, the high dispersion in water that causes sedimentation difficulties and sensitivity to the recombination of photoinduced electrons and holes also decreases its photocatalytic activity. Nevertheless, many studies have been reported using TiO₂ as photocatalyst for wastewater treatment against organic pollutants and pathogens [6–8]. The photocatalytic tests use TiO₂ as powder suspension or as thin films immobilized on different substrates. The major drawback of the TiO₂ powder dispersed in suspension systems is represented by the filtering expensive process necessary for the TiO₂ recovering [4, 9, 10]. Degussa P25 is a product commercially available in the market and represents one of the most used forms of TiO₂ composed of 70–80% anatase and 20–30% rutile crystallites with an average particle size of 25 nm. Degussa P25 is commonly used as a standard reference photocatalyst in order to compare the photocatalytic activity with other photocatalysts [4].

The TiO₂ photodegradation mechanism can be explained by the promotion of an electron in the conduction band (CB) under UV light resulting in a “hole” in the valence band (VB) and the formation of electron-hole (e⁻-h⁺) pairs. After losing the electron, the hole tries to recover the electron deficiency from the conduction band (recombination) or from the water adsorbed on the material’s surface. The interaction with water leads to the formation of hydroxyl radicals () which are able to oxidize any organic compound and finally to CO₂ and water [1, 7]. The electron from the CB has no hole to initiate the recombination process; thus the most rapid alternative to reduce is to form the superoxide radical anion () by reducing the oxygen adsorbed at the TiO₂ surface. The superoxide anion reacts with water to form more [7, 11].

The performance of TiO₂ based photocatalysts can be enhanced by doping with noble metals (Au, Ag, and Pt) [12] or several semiconductor compounds (In₂O₃, Cu₂S, CdTe, and NiO) [13–15] that improve the sensitivity of TiO₂ to visible light. Recent studies revealed that silver and silver nanoparticles (AgNPs) improve the photocatalytic activity of TiO₂ [16, 17] inducing an efficient surface plasmon resonance effect under sunlight preventing the recombination of e⁻-h⁺ pairs responsible for the decreasing process of the photocatalytic activity of TiO₂ [18, 19].

Therefore, the TiO₂/AgNPs hybrid materials can be activated for water disinfection and photodegradation by both UV and visible light based on three possible routes (Scheme 1) that associate the photocatalytic properties of TiO₂ (route I) with the antimicrobial and photocatalytic characteristics of AgNPs (route II) [17, 20] and the interaction between TiO₂ and Ag (route III).

Scheme 1: Possible routes for the photoactivity of TiO₂ AgNPs hybrid materials.

In this study, two methods were employed to obtain TiO₂ films doped with AgNPs with enhanced photoactivity. The first approach involved the synthesis of AgNPs solutions which were then used for realization of TiO₂ P25 dispersions in order to obtain films on a quartz tube followed by annealing. The size distribution influence on the enhancement of the photocatalytic activity was investigated. The second approach was aimed at simplifying the doping procedure. Thus, the manufacturing process consisted in the generation of AgNPs directly on the surface of TiO₂ P25 films and sinterization. The photodegradation activity of the films was investigated using methyl orange (MO) as target organic compound and TiO₂ as reference.

2. Experimental Procedures

2.1. Materials

AgNO₃ (ACS, Sigma-Aldrich), sodium borohydride (NaBH₄, Sigma-Aldrich), trisodium citrate dihydrate (Sigma-Aldrich), titanium dioxide (TiO₂ P25) (Degussa), methyl orange (MO) (Sigma-Aldrich), and acetic acid (Fluka) were used as received.

2.2. Methods

2.2.1. Ex Situ AgNPs Samples Synthesis (A, B, and C)

0.075 g (0.44 mmoles) AgNO₃ was dissolved in 200 mL ultrapure water in a round bottom flask maintained at 5°C. To this mixture, 0.4 g (1.36 mmoles) trisodium citrate dihydrate was added and the solution was stirred for 5 minutes, after which a solution of NaBH₄ (0.294 mmol/L) was introduced dropwise as follows in three different experiments: 0.3 mL (resulting sample A), 1.5 mL (resulting sample B), and 4 mL (resulting sample C), and the mixture was stirred for 30 minutes. The resulting AgNPs were used for the realization of the TiO₂ dispersions.

2.2.2. TiO₂ P25 Ex Situ AgNPs Film Realization

The TiO₂ P25 and TiO₂ P25/AgNPs films realization steps consist in the obtaining of stable dispersions, dip-coating of the quartz tube, and annealing at 500°C for 2 h.

3 g of TiO₂ P25 was well dispersed in 60 mL of AgNPs solution (A, B, or C) using an ultrasonic processor. The pH of the dispersion was adjusted to 4 using concentrated acetic acid.

For the reference TiO₂ P25 film ultrapure water was used for the realization of the dispersion and acetic acid for pH control. Prior to film deposition, the quartz tube was hydrophilized by immersion in a 5% NaOH solution overnight followed by rinsing with ultrapure water.

2.2.3. TiO₂ P25 AgNPs on Surface Generation

After obtaining by dip coating the TiO₂ P25 film on the quartz tube, the film was dried in oven at 80°C for 2 h and then immersed in solution A containing AgNO₃ (0.221 mmol/L) for 8 minutes after which it was introduced in solution B containing trisodium citrate (0.775 mmol/L) and NaBH₄ (0.0126 mmol/L). The obtained yellowish film is then sinterized in an oven at 500°C for 2 h.

2.3. Characterization

UV-VIS absorption spectra were recorded with an Able Jasco V-550 spectrophotometer; for the solid samples, reflection spectra were registered using an integrating sphere at normal incidence, a band width of 1 nm, and a scanning speed of 1000 nm min⁻¹.

The particle size measurement, through dynamic light scattering (DLS), was realized using a Nani ZS device (redbadge).

For the morphological characterization of the obtained TiO₂ and TiO₂ AgNPs films scanning electron microscopy analyses were performed using a FE-SEM (field emission-scanning electron microscope) RAITH e_Line at 10 kV acceleration voltage. The AgNPs morphology was investigated by TEM using a high resolution transmission electron FEI Tecnai F30 S-Twin microscope. A drop of the AgNPs suspension was mounted on a holey carbon film copper grid allowing the solvent to evaporate at room temperature.

2.4. Photodegradation Procedure

The photodegradation measurements were analyzed using a modified commercial set-up comprised of (a picture of the set-up is presented in Scheme 2):

(i)microdosing pump Masterflex-Unipan 335 A with a flow fixed at 350 mL/h,(ii)stainless steel jacket (21 cm) with a quartz tube core (used for photoactive material deposition) (the space between the jacket and the tube (180 cm³) was used for the dye solution circulation),(iii)UV-C lamp introduced inside the quartz tube (λ = 253.7 nm, power 4 W),(iv)collecting flask used as starting and end point for the dye solution,(v)silicon tubing connections used for connecting the collecting flask, pump, and reactor.

Scheme 2: The experimental set-up used for photocatalytic degradation.

For the photodegradation studies, 200 mL MO with a concentration of 0.5 mol/L was utilized.

3. Results

In order to obtain hybrid nanomaterials with photocatalytic activity, the first step was to synthesize different AgNPs and characterize their behavior. In Figure 1 is presented the color variation of the solutions from light yellow to brown-orange, due to the different size distribution and concentration of the AgNPs.

Figure 1: Samples A, B, and C of AgNPs solutions.

The first characterization of the AgNPs solutions consisted in UV-VIS analysis. The UV-VIS spectra presented in Figure 2 revealed a difference in absorbance and wavelength value. The wavelength value of the maximum absorption band is red-shifted between the samples which can be correlated with an increase of larger size particle content [21, 22]. Thus, sample A has the lowest values of both size and absorbance of AgNPs, followed by samples B and C, respectively.

Figure 2: UV-VIS spectra of AgNPs solutions A, B, and C.

DLS analysis was performed on the three solutions in order to obtain the mean diameter and size distribution of the AgNPs (Figure 3). For a more accurate size characterization, intensity and number of weighted mean diameters and distributions from DLS technique were considered. Although the whole range of diameters is shown in the intensity-weighted distribution (-distribution), the proportionality to the sixth power of diameter of particle () (  ∝  ) underestimates the small particles, which are only very weakly weighted [22, 23].

Figure 3: DLS analysis of A, B, and C AgNPs samples.

In the case of sample A, the DLS analysis revealed almost monodisperse AgNPs with a particle size range under 20 nm. From the DLS data, the weighted average diameter for sample A was estimated to be 12.6 nm. Sample B revealed two types of nanoparticles: the first presenting a weighted average diameter 13.6 nm while the second was calculated to be 83.6 nm. For sample C, the size polydispersity and weighted average diameter increased to around 24 nm with a small domain of larger particles. Thus, the main difference between the three samples is the increase in polydispersity and particle size from A to C, in the order A < B < C, respectively, and the decrease in content of particles less than 20 nm.

In order to confirm the particles size, TEM analyses have been performed. In Figure 4 it can be noticed that the DLS data are sustained by TEM images.

Figure 4: TEM images for the samples A, B, and C.

The next step of this study was directed to the synthesis and investigation of the hybrid material (TiO₂ P25/AgNPs films). The images from Figure 5 present the color variation of TiO₂ P25, respectively, the hybrid TiO₂ P25/AgNPs films after the deposition and annealing process on a quartz tube. The color of the hybrid material can be explained by the addition of the reflected wavelength domain of TiO₂ P25 and AgNPs.

Figure 5: Images of TiO₂ P25 and TiO₂ P25/AgNPs films after deposition and annealing on the quartz tube.

In order to characterize this color modification, the films obtained using TiO₂ P25 and the three AgNPs solutions (A, B, and C) were analyzed by UV-VIS (Figure 6). The obtained TiO₂ P25/AgNPs hybrid films registered different reflection bands compared with the reference (TiO₂ P25 film). The absorption bands are blue-shifted, while the AgNPs size distribution decreases (see inset). This can be explained by the overlaying of the adsorption bands of TiO₂ P25 film and different AgNPs particle size distribution. Thus, the registered signals are in good correlation with the results registered by DLS analysis (Figure 1) and UV-VIS analysis (Figure 1) of the initial AgNPs solutions.

Figure 6: The UV-VIS spectra of the hybrid films.

The concentration of TiO₂ P25 is much higher than that of the AgNPs; therefore the spectroscopic influence of silver nanoparticles is rather minor on the UV-VIS absorption properties of the films; however, all the samples present absorption at a lower wavelength compared to the initial TiO₂ P25. Thus, the hybrid material is photoactive for a larger wavelength domain.

The photocatalytic activity of the hybrid nanocomposite films was determined using the experimental set-up presented in Scheme 2 (details on the procedure are presented in Section 2.4). The most important element of our experiment was the reactor equipped with the quartz tube and illuminated with an UV lamp.

The kinetics of photocatalytic degradation and the percentage of MO photodegraded are highly dependent on AgNPs size. The highest photocatalytic activity was registered for the nanoparticles with the smallest size and narrower particle size distribution (sample A) (see DLS analysis, Figure 3).

Furthermore, in all three cases involving the hybrid materials, although the size of AgNPs nanoparticles increases, the photocatalytic activity registered superior values compared with the TiO₂ P25. Thus, after 150 min, the photodegradation percentage reaches 33%. The degradation curves are linear confirming a first order reaction degradation kinetics mechanism which allowed the utilization of the Langmuir-Hinshelwood model [24, 25] for determination of the apparent reaction constant (Figure 7). All the samples have presented adsorption characteristics similar to TiO₂ P25 for the “in the dark” study.

(a)

(b)

(c)

Figure 7: (a) Photodegradation kinetics; (b) percentage of decomposed MO versus maximum absorption wavelength value of the AgNPs solution; (c) values of apparent decomposition constant.

The analysis of the photodegradation results proved that the materials based on AgNPs improve the photoactivity of the TiO₂ films. The introduction of AgNPs in the TiO₂ P25 suspension increased the photodegradation of MO in all cases, regardless of the AgNPs size distribution.

For this reason, the next approach of this study aimed to increase the contact surface between TiO₂ P25 and AgNPs, simplifying the manufacturing process. Thus, in order to validate this method, AgNPs were generated directly on the surface of TiO₂ P25 film and the photoactivity of the obtained hybrid material was analyzed using MO.

In Figure 8, the SEM images of the TiO₂ P25 and for the new hybrid material are presented comparatively.

(a)

(b)

Figure 8: SEM images of TiO₂ P25 (a) and AgNPs generated on the surface of TiO₂ P25 (b).

The SEM analysis reveals that AgNPs generated on the TiO₂ P25 surface form aggregates in different areas (Figure 7(b)) (red highlighted). Although their formation was preferential, the contact area with MO is enlarged and should register higher efficiency values.

The evolution of the decomposition process of the dye is presented in Figure 8. For a better investigation of the hybrid film, the results were compared with a simple TiO₂ P25 and the generated AgNPs/TiO₂ P25 film in the dark. From Figure 9, the film is very stable in the dark and the MO was not decomposed. The hybrid film resulting from the generation of AgNPs directly on TiO₂ P25 registered a photodegradation capacity of MO of 45% after 150 min.

Figure 9: The photodegradation evolution of MO in the presence of AgNPs generated directly on TiO₂ P25 film.

This approach of reducing silver on the surface of TiO₂ P25 increased the direct contact of AgNPs with the contaminated medium which determined a higher efficiency of the degradation process, sustaining also the possible photodegradation mechanism of the dye.

4. Conclusions

The aim of the present study consisted in the obtaining of hybrid material films, using TiO₂ P25 and AgNPs. In the first case (mixing TiO₂ P25 with AgNPs solutions), the size distribution of the AgNPs proved to be a key element in the photodegradation activity of the materials; the main difference between the three samples is the increase in polydispersity and particle size from A to C, in the order A < B < C, respectively, and the decrease in content of particles less than 20 nm. For the first case, the degradation of MO is about 33% after 150 min under UV irradiation.

The second approach involved the generation of AgNPs on the surface of the TiO₂ P25 film. In this case, the contact surface of AgNp with MO is higher and the photodegradation activity increased to 45% after 150 min.

Conflict of Interests

The authors Tomkouani Kodom, Edina Rusen, Ioan Călinescu, Alexandra Mocanu, Raluca Şomoghi, Adrian Dinescu, Aurel Diacon, and Cristian Boscornea declare that there is no conflict of interests regarding the publication of this paper.

Acknowledgments

Tomkouani Kodom would like to thank the postdoctoral Scholarships Programme “Eugen Ionescu” of the Francophony University Agency (AUF) for financial support. Aurel Diacon and Alexandra Mocanu acknowledge financial support from the Sectoral Operational Programme Human Resources Development 2007–2013 of the Ministry of European Funds through the Financial Agreements POSDRU/159/1.5/S/132395 and POSDRU/159/1.5/S/132397.

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