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Valorization of rambutan peel for the synthesis of silver-doped titanium dioxide (Ag/TiO2) nanoparticles

  • Brajesh Kumar

    Brajesh Kumar is currently working as a Prometeo Researcher in the Centro de Nanociencia y Nanotecnologia, Universidad de las Fuerzas Armadas ESPE, Ecuador. He received his MSc and PhD in Chemistry from the University of Delhi, India. His research interest is the development of sustainable and ecofriendly techniques for natural product extraction, purification and analysis, nanoparticles synthesis and their applications for environmental remediation, active films of organic solar cells, nanomedicine, sensors and organic synthesis.

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    , Kumari Smita

    Kumari Smita completed her Master’s degree in inorganic chemistry at Ranchi University, India. She worked as a senior research assistant at the National Metallurgical Laboratory, Jamshedpur, India for 6 years and has been associated with Centro de Nanociencia y Nanotecnologia for the last 3 years. Her current research interest focuses on the development of green and sustainable processes for the synthesis of nanoparticles, nanocomposites and remediation of, for example, organic dyes, heavy metal ions.

    , Yolanda Angulo

    Yolanda Angulo received the title of Physicist in 2007 at the National Polytechnic School, Ecuador. She completed her doctorate in physical sciences at the Catholic University, Rio de Janeiro, Brazil in 2012. She specialized in growth of thin films and manufacture of organic and hybrid devices, as well as their characterization. From 2012, she has been working at the University of the Armed Forces ESPE and is a member of the Center for Nanoscience and Nanotechnology and of the Society of Optics and Photonics of Ecuador.

    and Luis Cumbal

    Luis Cumbal received his PhD from Lehigh University, USA. He has been dedicated to researching and developing new materials to be applied in the environmental remediation of soils and water. Currently, Dr. Cumbal is the Director of the Center for Nanoscience and Nanotechnology and Professor of the Department of Life Sciences at the Universidad de las Fuerzas Armadas, Ecuador.

Published/Copyright: June 22, 2016
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Abstract

In this article, silver-doped titanium dioxide nanoparticles (Ag/TiO2 NPs) were synthesized in an ecologically and economically favorable way using rambutan (Nephelium lappaceum L.) peel extracts along with the study of its photocatalytic activity on methylene blue (MB) dye and antioxidant efficacy against 1,1-diphenyl-2-picrylhydrazyl (DPPH·). A wide range of analytical techniques including UV-vis spectroscopy, transmission electron microscopy (TEM), dynamic light scattering (DLS), X-ray diffraction (XRD), and Fourier transform infrared (FTIR) spectroscopy analysis were performed to ascertain the synthesis of Ag/TiO2 NPs. The synthesized Ag/TiO2 NPs enhanced the photocatalytic degradation of MB (81.6%, k=0.002495 min-1) under direct solar light irradiation. The results showed that discarded agricultural waste as rambutan peel can be utilized as natural bioreductant in future materials science applications.

1 Introduction

Over the past few decades, titanium dioxide nanoparticles (TiO2 NPs) have attracted remarkable research interest in the scientific community, and consequently several reports have shown the utility of TiO2 NPs and different metals (Pt, Au, Ag and Pd) doped TiO2 NPs at various fields, such as catalysis [1], [2], solar cells [3], gas sensors [4], [5], semiconductors [6], optical devices [7], fuel cells [8], etc. In general, noble metal doping of TiO2, extends its light absorption into the visible region and manipulates the band gap energy of TiO2 which enhances the efficiency of photocatalytic reactions [9]. Several physical, chemical and biological methods [10], [11], [12] have been developed for their synthesis and used for the degradation of dyes in the presence of UV or visible light. Among all doped nanoparticles, silver-doped TiO2 NPs (Ag/TiO2 NPs) are of special interest in industrial applications due to their nontoxicity, low cost and availability [13]. Green synthesis of nanoparticles is gaining importance and has been suggested as a possible alternative to chemical and physical methods [14], [15].

Nevertheless, there are very few reports concerning the synthesis of Ag/TiO2 NPs using biological reductants and templates by the green route method [12]. Rambutan (Nephelium lappaceum L.), a tropical fruit, originated from Southeast Asia and is generally consumed fresh, in juices, jams, jellies, marmalades, etc. It is also known as Achotillo, Hairy lychee, Mamón Chino, Shao-Zi, etc., in different parts of the world and its peel is rich in anthocyanins, ellagitannins, ellagic acid, corilagin, geraniin, syringic acid and p-coumaric acid, a good source of natural antioxidants [16]. The role of rambutan peel extract (RPE) as a reducing and capping agent, mediating synthesis of Ag/TiO2 NPs is summarized in Figure 1.

Figure 1: Schematic diagram for synthesis of silver-doped titanium dioxide nanoparticles (Ag/TiO2 NPs) using rambutan peel extract (RPE).
Figure 1:

Schematic diagram for synthesis of silver-doped titanium dioxide nanoparticles (Ag/TiO2 NPs) using rambutan peel extract (RPE).

So, the development of an efficient synthesis of doped nanoparticles in an ecologically and economically favorable way is a great challenge in modern nanoscience. In the present study, Ag/TiO2 NPs were synthesized by RPE, and characterized using UV-vis spectroscopy, transmission electron microscopy (TEM), dynamic light scattering (DLS), X-ray diffraction (XRD), and Fourier transform infrared (FTIR) spectroscopy techniques. Further, the photocatalytic activity of Ag/TiO2 NPs in the presence of solar light for the degradation of methylene blue (MB) and antioxidant activity against 1,1-diphenyl-2- picrylhydrazyl (DPPH·) has been investigated. MB is a thiazine based cationic dye, commonly used as dyeing materials for cotton, silk, paper and wood. Its acute exposure can cause some harmful effects to human (vomiting, shock, cyanosis, jaundice, etc.) and the aquatic environment [14]. Thus, remediation of MB from wastewater is very important.

2 Materials and methods

2.1 Materials and synthesis of Ag/TiO2 NPs

Fresh Rambutan fruit was purchased from the popular market near Universidad de las Fuerzas Armadas ESPE, Sangolqui, Ecuador. After being washed thoroughly, Rambutan fruit peel (5 g) was cut finely and heated (60–62°C) in 50 ml of deionized water for 60 min. After cooling, the dark red color RPE was filtered using Whatman No. 1 paper, England and stored at 4°C for further use. TiO2 (99%, anatase) and DPPH· (>99.5%) were purchased from Sigma Aldrich, USA. Silver nitrate (AgNO3, 99.0%) as the source of Ag+ ion and MB (99.5%) were purchased from the Spectrum, USA. Milli-Q water was used in all experiments. The Ag/TiO2 NPs were synthesized based on the reduction of AgNO3 in a TiO2 suspension. RPE (2 ml) was sonicated with ultrasonic processors (DAIGGER GE 505, 500 W, 20 kHz) for (5 min, 72%, 30 s pulse on/off) immersed directly into a 12 ml solution of AgNO3 (1 mm, 10 ml) and TiO2 (5 mm, 2 ml), then stirred at room temperature (22–25°C) for 24 h until the color of the reaction mixture changed from turbid white to light brown.

2.2 Photocatalytic degradation activity

In order to evaluate the photocatalytic performances of Ag/TiO2 NPs, photocatalytic degradation of MB under solar light irradiation (850–936 cd/m2) was performed. In the reaction set 1, 10 ml of MB (10 mg/l) was mixed with 2 ml H2O and in another set 2, 10 ml MB (10 mg/l), Ag/TiO2 NPs (250 μl) and H2O (1750 μl) were mixed vigorously for 10 min in the dark to reach an adsorption-desorption equilibrium. Then, both sets were kept in the direct sunlight (solar light) and progress of the reaction was monitored at different time intervals. Finally, the rate of MB dye degradation was monitored by measuring the absorption of MB in the filtrate at the wavelength 664 nm, before and after degradation using a UV-vis absorption spectrometer. Photocatalytic degradation percentage of MB was calculated using Eq. (1):

(1)η=A0-AtA0×100% (1)

where η is the rate of degradation of MB in terms of percentage, A0 is the initial absorbance of the dye solution and At is the absorbance of the MB at time t.

2.3 Antioxidant activity

The antioxidant activity of the Ag/TiO2 NPs was measured by the DPPH· assay using a method by Kumar et al. [16], [17] with slight modification. The DPPH· is a stable free radical with purple color and its activity is inhibited due to donation of electrons by an antioxidant molecule. An aliquot (1000–200 μl) of Ag/TiO2 NPs or control and (1000–1800 μl) of H2O was mixed with 2000 μl of DPPH· (0.2 mm in 96% ethanol). The mixture was vortexed vigorously and allowed to stand at room temperature for 30 min in the dark. Absorbance of the mixture was measured spectrophotometrically at 517 nm, and the free radical scavenging activity was calculated using Eq. (2):

(2)Scavenging effect (%)=[1-{absorbance of sample/absorbance of control}]×100 (2)

The scavenging percentages of all samples were plotted. The final result was expressed as % of DPPH· free radical scavenging activity (ml).

2.4 Characterization of Ag/TiO2 NPs

The UV-vis spectrum was measured using a Thermo Spectronic, GENESYS 8, England spectrophotometer. Size and selective area electron diffraction (SAED) patterns of nanoparticles were studied on TEM (FEI, Tecnai, G2 spirit twin, Holland). The particle size distributions of nanoparticles were determined using the Horiba, DLS Version LB-550 program, Japan. XRD studies on thin films of the nanoparticles were carried out using a PANalytical brand θ–2θ configuration (generator-detector) X-ray tube copper λ=1.54 A° and an Empyrean diffractometer. FTIR-ATR spectra were recorded on a Spectrum Two IR spectrometer (Perkin Elmer, USA).

3 Results and discussion

3.1 Visual and UV-vis analysis

As shown in Figure 2, reduction of the Ag+ to AgNPs on the surface of TiO2 using RPE could be followed by the appearance of a brown color, due to excitation of plasmon resonance in AgNPs [1], [2], [16]. Before doping, TiO2 did not show any significant absorption peak in the range of 350–500 nm, but after doping with Ag+, the UV-vis spectra showed an increase of absorbance and appearance of new peaks in the range of 370–460 nm (showed a red shift). The red shift of the absorption curve results in a reduction of the band gap energy and also the recombination rate, and hence, enhanced photocatalytic activity. These results agreed with the observation reported by Gupta et al. [18].

Figure 2: UV-vis spectrum of silver-doped titanium dioxide nanoparticles (Ag/TiO2 NPs) synthesized by rambutan peel extract (RPE).
Figure 2:

UV-vis spectrum of silver-doped titanium dioxide nanoparticles (Ag/TiO2 NPs) synthesized by rambutan peel extract (RPE).

3.2 TEM and DLS analysis

The approximate size, shape, and size distribution of particles were characterized using TEM and DLS. The TEM image (Figure 3A) of TiO2 particles was found to be almost spherical in shape and about 100–180 nm, respectively. Figure 3B and C show that the Ag/TiO2 NPs have a strong interaction with the biomolecules of the RPE and the majority of Ag/TiO2 NPs were agglomerated in addition to small Ag particles. From the morphological point of view, Ag/TiO2 NPs showed a spherical shape with a size range of 30–200 nm, and Ag particles (black dots indicated) were located on the surface of the individual TiO2 NPs (size of Ag<TiO2). This result is very similar to the Ag loaded TiO2 NPs reported by Anandan et al. [19]. The SAED patterns (Figure 3C′) show circular diffraction patterns, which are indicative of the crystalline nature of the Ag/TiO2 NPs, and are in good agreement with the XRD data. The DLS size distribution of Ag/TiO2 NPs (Figure 3D) showed that the average size of Ag/TiO2 NPs is 163.3±249.2 nm, which is a slight deviations from the results obtained from the TEM analysis. This is due to the agglomeration of NPs, screening of small particles by bigger ones and attachment of RPE biomolecules on the surface of Ag/TiO2 NPs [20].

Figure 3: Transmission electron microscopy (TEM) micrograph of (A) titanium dioxide nanoparticles (TiO2 NPs), (B, C) silver-doped titanium dioxide nanoparticles (Ag/TiO2 NPs), (C′) selective area electron diffraction (SAED) pattern of Ag/TiO2 NPs and (D) dynamic light scattering (DLS) size distribution pattern of Ag/TiO2 NPs.
Figure 3:

Transmission electron microscopy (TEM) micrograph of (A) titanium dioxide nanoparticles (TiO2 NPs), (B, C) silver-doped titanium dioxide nanoparticles (Ag/TiO2 NPs), (C′) selective area electron diffraction (SAED) pattern of Ag/TiO2 NPs and (D) dynamic light scattering (DLS) size distribution pattern of Ag/TiO2 NPs.

3.3 XRD and FTIR analysis

The XRD patterns of the as-synthesized Ag/TiO2 NPs are shown in Figure 4A. The peaks located at 2θ values of 25.295°, 37.943° and 48.085°, can be indexed to (101), (112) and (200) diffractions of the anatase phase of TiO2 (ICSD No. 98-002-4276). The diffraction peaks originating from Ag are hardly detected in the Ag/TiO2 NPs, although the XRD peak at 37.9° is a common diffraction peak for both counterparts and Ag peaks overlapped with those of TiO2. It also suggests a successful reduction of Ag+ into Ag nanoparticles on the surface of the TiO2 crystallites [21], [22]. Another peak observed at 29.847° is due to the low crystallinity of the organic biomolecules and the broadened diffraction peaks indicate that the sizes of the Ag/TiO2 NPs are small. The FTIR spectra provided information on the nature of the produced Ag/TiO2 NPs. As shown in Figure 4B, the absorption peaks at 3270 cm-1 and 2924 cm-1 are attributed to the stretching mode of hydroxyl O-H and aliphatic C-H groups, respectively [15]. The absorption peaks at 1633 cm-1 corresponds to bending vibration of H-O-H bond on TiO2 [23] and C=O stretching vibration, whereas the peaks at 1417 cm-1, 1318 cm-1 and 1245 cm-1 indicate the C=C and C-O stretching vibrations of flavonoids/phenolic groups of RPE [16]. The high intensity at 1030 cm-1 corresponds to secondary -OH vibrations and the broad spectrum below 700 cm-1 reveals the existence of metal oxide vibrations, including Ag-O, Ti-O and Ag-O-Ti [23]. The XRD and FTIR results confirm the formation of the Ag/TiO2 NPs using RPE.

Figure 4: (A) X-ray diffraction patterns and (B) Fourier transform infrared (FTIR) spectrum of silver-doped titanium dioxide nanoparticles (Ag/TiO2 NPs).
Figure 4:

(A) X-ray diffraction patterns and (B) Fourier transform infrared (FTIR) spectrum of silver-doped titanium dioxide nanoparticles (Ag/TiO2 NPs).

3.4 Photocatalytic activity

The photocatalytic activity of Ag/TiO2 NPs is evaluated by the degradation of MB in aqueous solution. The prominent peak intensity of MB (λmax=664 nm) decreases gradually with the addition of a very low quantity of Ag/TiO2 NPs under sunlight and shows more than 81% degradation within 600 min (Figure 5A). Pure TiO2 has low photocatalytic activity under solar light, due to its wide band gap. So, Ag/TiO2 NPs improved the photodegradation efficiency compared to pure TiO2. The rate of MB degradation catalyzed by Ag/TiO2 NPs assumed to be fitted by a first order rate law [15], shows a linear relationship between ln (A0/At) and reaction time (t) and the slope gives the rate constant (K) (Figure 5B). The observed “K” is 0.00249545 min-1. The basic mechanism behind the degradation of MB is that photogenerated limited charges can generate ·OH radicals and O2· intermediate species by reacting with adsorbed H2O molecules for the photodecomposition of MB [24]. Ag can act as an electron trap and promote the interfacial charge transfer processes in the composite systems, which reduces the recombination of the photo-induced electron-hole pairs, thus improving the photocatalytic activity of TiO2 [25].

Figure 5: (A) Solar light-induced photocatalytic degradation and (B) first order kinetic plot of methylene blue (MB) using the silver-doped titanium dioxide nanoparticles (Ag/TiO2 NPs).
Figure 5:

(A) Solar light-induced photocatalytic degradation and (B) first order kinetic plot of methylene blue (MB) using the silver-doped titanium dioxide nanoparticles (Ag/TiO2 NPs).

3.5 Antioxidant activity

Antioxidant activity refers to the inhibition of the reactive oxygen species including hydroxyl radicals, peroxyl radicals, super oxide radicals, hydrogen peroxide, singlet oxygen, and various lipid peroxides, that play an important role in the initiation and progression of various diseases [26]. In Figure 6, it was found that the DPPH· scavenging activity of RPE decreased less significantly in comparison to Ag/TiO2 NPs with increasing doses and also demonstrated a higher antioxidant activity than Ag/TiO2 NPs. The maximum scavenging efficacies for the RPE and Ag/TiO2 NPs were found to be 91.80% and 70.65%, respectively, in 0.2 ml. This is due to the plant extract itself being responsible for the majority of the antioxidant activity, whereas, Ag/TiO2 NPs are less soluble and undergo agglomeration and sedimentation, which causes an increase in the particle size and decrease in specific surface area. In general, chemically synthesized nanoparticles are not contributing much to the antioxidant activity, but Ag/TiO2 NPs showed antioxidant efficacy, which may be attributed due to the adsorption of biomolecules of RPE over spherically shaped Ag/TiO2 NPs [16], [27].

Figure 6: Antioxidant activity of (A) rambutan peel extract (RPE) and (B) silver-doped titanium dioxide nanoparticles (Ag/TiO2 NPs).
Figure 6:

Antioxidant activity of (A) rambutan peel extract (RPE) and (B) silver-doped titanium dioxide nanoparticles (Ag/TiO2 NPs).

4 Conclusions

In conclusion, an RPE mediated eco-friendly and low cost approach has been used for the synthesis of Ag/TiO2 NPs which resulted in spherical particles of the average size of 30–200 nm. Also, a variety of analytical techniques, including UV-vis, TEM, DLS, XRD and FTIR, were used to characterize as-synthesized nanoparticles in detail. The results showed that the discarded agricultural waste product, RPE encapsulated Ag/TiO2 NPs can be utilized as an alternative agent for removal of MB (>80%) and antioxidant agent at very low concentrations.

About the authors

Brajesh Kumar

Brajesh Kumar is currently working as a Prometeo Researcher in the Centro de Nanociencia y Nanotecnologia, Universidad de las Fuerzas Armadas ESPE, Ecuador. He received his MSc and PhD in Chemistry from the University of Delhi, India. His research interest is the development of sustainable and ecofriendly techniques for natural product extraction, purification and analysis, nanoparticles synthesis and their applications for environmental remediation, active films of organic solar cells, nanomedicine, sensors and organic synthesis.

Kumari Smita

Kumari Smita completed her Master’s degree in inorganic chemistry at Ranchi University, India. She worked as a senior research assistant at the National Metallurgical Laboratory, Jamshedpur, India for 6 years and has been associated with Centro de Nanociencia y Nanotecnologia for the last 3 years. Her current research interest focuses on the development of green and sustainable processes for the synthesis of nanoparticles, nanocomposites and remediation of, for example, organic dyes, heavy metal ions.

Yolanda Angulo

Yolanda Angulo received the title of Physicist in 2007 at the National Polytechnic School, Ecuador. She completed her doctorate in physical sciences at the Catholic University, Rio de Janeiro, Brazil in 2012. She specialized in growth of thin films and manufacture of organic and hybrid devices, as well as their characterization. From 2012, she has been working at the University of the Armed Forces ESPE and is a member of the Center for Nanoscience and Nanotechnology and of the Society of Optics and Photonics of Ecuador.

Luis Cumbal

Luis Cumbal received his PhD from Lehigh University, USA. He has been dedicated to researching and developing new materials to be applied in the environmental remediation of soils and water. Currently, Dr. Cumbal is the Director of the Center for Nanoscience and Nanotechnology and Professor of the Department of Life Sciences at the Universidad de las Fuerzas Armadas, Ecuador.

Acknowledgments

This scientific work has been funded by the Universidad de las Fuerzas Armadas ESPE and Prometeo Project of the Ministry of Higher Education, Science, Technology and Innovation (SENESCYT), Ecuador.

  1. Conflict of interest statement: The authors declare that there is no conflict of interests regarding the publication of this article.

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Received: 2016-1-4
Accepted: 2016-3-29
Published Online: 2016-6-22
Published in Print: 2016-8-1

©2016 Walter de Gruyter GmbH, Berlin/Boston

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