Abstract

Direct synthesis of gold nanoparticles (AuNPs) on cellulose fiber has been successfully performed via facile green approach using lignin-containing unbleached kraft softwood pulp. The resulting AuNPs composited fibers showed apparent color change from pale yellow to purplish-dark brown by varying the amount of gold ions (Au3+) due to the surface plasmon resonance of nanogold. Further confirmation of AuNP formation on the fiber surface was conducted by UV-Vis diffuse reflectance spectroscopy (DRS), X-ray diffraction (XRD), and field emission scanning electron microscopy (FE-SEM). X-ray photoelectron spectroscopy (XPS) analysis revealed that gold nanoparticles formed on the fiber are well-defined pure metallic gold, indicating that Au3+ ions are efficiently bioreduced into Au0 and bind to the fiber surface. Antioxidant activity was evaluated by decomposition of 2,2-diphenyl-1-picryl-hydrazyl (DPPH) in dark and light condition. As-prepared unbleached kraft fiber-AuNP composite showed significantly enhanced antioxidant activity and its DPPH scavenging rate reached about 86.05%.

1. Introduction

Nowadays the contemporary consumers are not purchasing only a product, but a solution for healthier and safer food [1]. The shelf life of fatty foods and dry grains is profoundly affected by the formation of active free radicals (e.g., reactive oxygen species). Reduction or termination of the lipid oxidation provides longer shelf life product and traditionally, antioxidants are coated on food surface or mixed into initial food formulations. However, lack of selectivity to the food surface and the side reactions between food system and antioxidant active compounds limit the use of these approaches [2]. Antioxidant active packaging alternatively plays a crucial role in inhibiting the oxidative rancidity in food by scavenging the free radicals generated by the oxidative processes.

Gold nanoparticle (AuNP), a human trace element, has gained much more attention and tremendous works in pharmacological sectors and biomedical applications due to its unique therapeutic activity, being inert, and nontoxic nature [3]. AuNP has drawn enormous attention as one of the most effective heterogeneous catalysts, particularly, for selective oxidation [4, 5]. There is also considerably interest in using AuNP for both in vitro and in vivo antioxidant application [68]. BarathManiKanth et al. [9] disclosed the effectual role of AuNP as an antioxidative agent for lipid peroxidation and reactive oxygen species in diabetic mice. Balasubramani et al. [10] showed that AuNP is highly capable of scavenging free radicals which lead to anticancer property. This study proposed an alternative application of AuNP as a drug in nanomedicine to treat breast cancer in the future. Moreover, Leu et al. [11] investigated the effects of AuNP combined with epigallocatechin gallate and α-lipoic acid in wound healing. They found that the treatment of cutaneous wound in mice can be accelerated by antioxidation effect of AuNP compound. Therefore, regarding unique antioxidation characteristic of nanogold, the advancements in use of AuNP for potential antioxidant food packaging may bring new innovative to active packaging.

A wide range of methods have been developed to produce AuNP in a multitude of chemical and physical processes [12, 13]. The traditional and most widely used method for the synthesis of AuNP commonly involves the reduction of a soluble metal salt by a reducing agent or high-temperature gaseous conditions. Hydrazine, tri-sodium citrate, sodium borohydride, and dimethylformamide are examples of reported reducing and stabilizing agents [14, 15]. However, exposure to these highly reactive chemicals poses potential risks to human health and the environment [16].

Enormous efforts have been made to integrate green chemistry concepts to metal nanoparticle syntheses, without accumulating an enormous quantity of toxic chemicals in the environment [17, 18]. Natural resources such as plant extracts, microorganisms, biodegradable polymers, and polysaccharides are known to be effective biological materials for alternative green syntheses of metallic nanoparticles [19, 20]. Among the various greener reagents, polysaccharides are quite advantageous when utilized in green synthesis due to the fact that they have an abundance of hydroxyl groups and hemiacetal reducing ends; thus, they can be used as both reducing and stabilizing agents for metal nanoparticles [21]. Various polysaccharides such as buffered glucose incorporated with starch [22], chitosan associated with organic acid [23], cellulose in ionic liquid [24], guar gum [25], dextran [26], pullulan [27], and arabinoxylan [28] have been employed for AuNP synthesis.

More recently, there has been considerable interest in the direct synthesis of metal nanoparticles on fibers, since gold colloids easily aggregate to yield bulkier materials, which in turn lowers the optical and catalytic activities [29]. Zhang et al. [30] developed AuNPs embedded in a biotemplate using a single-step method in which AuNPs were synthesized by polyethyleneimine and simultaneously coated on bacteria cellulose. Johnston and Nilsson [31] have proposed a green reduction mechanism and immobilization of nanosilver and nanogold using unbleached lignin-containing paper fibers. Aromatic methoxy and phenol groups of lignin were found to reduce Au3+ to Au0 and to firmly bind AuNPs to the fiber surface. In addition, Azetsu et al. [32] demonstrated the direct synthesis of AuNPs by TEMPO-oxidized softwood kraft paper. The aldehydic moieties in carbohydrates were reported as a reducing agent, while obtained AuNPs were deposited on cellulose fibers.

Despite several pathways of AuNP green synthesis, there is still great interest in developing a simple and sustainable method to prepare well-defined gold nanoparticles on renewable cellulose-based fibers without the use of additional reducing chemicals and fiber modification. To date, few studies have focused on such techniques. Here we report a facile biosynthesis of AuNP using unbleached kraft softwood fiber which acts as both reducing-stabilizing agent and substrate for the AuNP immobilization. UV-Vis diffuse reflectance spectroscopy (DRS), X-ray diffraction (XRD), field emission scanning electron microscopy (FE-SEM), energy dispersive spectroscopy (EDS), and X-ray photoelectron spectroscopy (XPS) were used to characterize the resulting fiber-AuNPs composite. The antioxidant activity of the AuNPs composite sheets was investigated by measuring the scavenging rate of 2,2-diphenyl-1-picryl-hydrazyl (DPPH) as an indicator.

2. Experimental

2.1. Materials

ACS reagent grade hydrogen tetrachloroaurate(III) trihydrate (HAuCl4·3H2O, chloroauric acid) was used as received from Alfa Aesar (Ward Hill, IL, USA) in the preparation of AuNPs on the fiber. Unbleached softwood kraft pulp was obtained from Dongli Paper (Ansan, Korea). 2,2-Diphenyl-1-picryl-hydrazyl (DPPH) was purchased from Sigma Chemical Co. (St. Louis, MO, USA). Ultra-pure water with a specific resistivity of 18 MΩ·cm was used in this study.

2.2. Biosynthesis of AuNP on Unbleached Kraft Pulp

AuNPs composite fibers were simply prepared by a greener route using unbleached kraft pulp. An aqueous solution of chloroauric acid as the AuNP precursor was prepared at various concentrations ranging up to 40 mM by dissolving HAuCl4·3H2O in ultra-pure water. The unbleached softwood kraft pulp was first disintegrated with a valley beater according to the Technical Association of the Pulp and Paper Industry (TAPPI) test method T 200 sp-01 [33]. The pulp was then mechanically refined to approximately 430 mL of Canadian Standard Freeness (CSF) according to TAPPI test methods T 227 om-04 [34] and T 200 sp-01 prior to biosynthesis of nanogold. In a typical synthesis of AuNPs on the fibers, 2 g of refined wet pulp with approximately 90% moisture content was suspended in 40 mL of chloroauric acid aqueous solution with constant stirring until it was completely dispersed (0.5% consistency, 0.5 g dried pulp/L). Following preparation of the pulp suspension, in order to facilitate AuNP synthesis via reduction of Au3+ to Au0, the mixture of pulp fibers and chloroauric acid was subsequently placed in an autoclave at 15 psi and 121°C for 30 min. After the reaction was complete, AuNPs composite cellulose fibers were centrifuged and rinsed repeatedly with DI water followed by suctioning on a 200-mesh wire to form a wet sheet. The obtained fiber-AuNPs composite sheet was dried at 60°C under vacuum overnight. Finally a purplish to red-brownish colored AuNPs conjugated papers were obtained. Paper made of only unbleached kraft pulp, denoted by unbleached kraft paper (UBK), was also prepared for use as a reference sample. In order to quantify the amount of Au synthesized on cellulose fiber, the EDS analysis on the surface of as-prepared UBK-AuNPs composites has been performed. As a result, amount of Au was confirmed as 1.9 wt% and 5.3 wt%.

2.3. Characterization of Cellulose-AuNP Composite

UV-Vis diffuse reflectance spectra were recorded on a UV-Vis spectrophotometer (V-600, Jasco, Japan) with an attached integrating sphere. A barium sulfate (BaSO4) pellet was used as a reference to measure absorption of as-prepared cellulose fiber-AuNP composite sheets. X-ray diffraction patterns were obtained with a Bruker D2 Phaser with a Ni-filtered Cu Kα radiation source (λ = 0.15418 nm) using a 1 mm equatorial slit and 3 mm air scattering slit. The surface morphology of the composite sheets was observed by field emission scanning electron microscopy (FESEM Quanta FEG 250, FEI Co., Ltd., USA) in backscattered electron (BE) mode after sputtering Pt/Pd onto the specimen. FTIR analyses were performed using a Spectrum 65 FTIR (Perkin Elmer, USA). Each spectrum was collected in attenuated total reflectance (ATR) mode with 2 cm−1 resolution for 16 scans in the wavenumber range of 4000–400 cm−1. XPS data were obtained using a Kratos AXIS ULTRA XPS system with a monochromated Al KαX-ray source. Samples were mounted in the sample chamber on double-sided copper tape (3 M) at an ultra-high vacuum (UHV) chamber operating pressure of 10−8 Torr. To investigate the surface chemistry of both the reference and UBK-AuNPs composite, survey and high-resolution spectra were processed using CasaXPS software from which a Shirley background was subtracted before fitting the spectra peaks to a symmetric Gauss-Lorentz sum function. All spectra were calibrated to the binding energy of C 1s photoelectrons at 284.6 eV.

2.4. Evaluation of Antioxidant Property

Cellulose fiber-AuNP composite sheets were subjected to the determinations of the DPPH radical scavenging ability in both light and dark condition. Samples were cut into small pieces (approximately 3.0 × 3.0 mm) followed by immersing in 5.0 mL of dark purple-colored DPPH solution (100 μmol/L in absolute ethanol). It was then placed and constantly shaken on a twist shaker (TW3, FINEPCR, Seoul, Korea) at ambient temperature for 180 min. Three replicates and UBK as control sample were prepared for each condition. The radical scavenging rate was measured with the absorbance of DPPH at 516 nm wavelength on UV-Vis spectrum. The antioxidant activity was calculated with the following equation: where was the absorbance of the fresh DPPH solution and was the absorbance of the test sample at reaction time, 180 min.

3. Results and Discussion

This study demonstrated a simple green reduction method to prepare cellulose fiber-AuNP nanocomposites using unbleached kraft pulp. During the reduction of Au3+ by lignin-containing unbleached cellulose fibers, the color of the pulp slurry obviously changed and progressively deepened with increasing chloroauric acid concentration. Figure 1 shows digital images of composite sheets along with the pulp slurry, which presents the apparent change in color of fibers from pale brown to purple and wine-red brown as the concentration of chloroauric acid was increased. This diverse color change is attributed to the surface plasmon resonance (SPR) of AuNPs [3537], implying the direct formation of nanogold on the fiber surface.

Figure 2 presents the UV-Vis diffuse reflectance spectra of as-prepared UBK-AuNPs composite sheets. Unbleached kraft paper was used as a comparative reference, which showed broad absorption in the UV region below 400 nm. All of the cellulose fiber-AuNPs composite spectra exhibited a strong absorption peak at 539 nm corresponding to a characteristic SPR absorption band of gold nanoparticles. The peak was more symmetric and narrower with increasing concentrations of gold precursor, which indicates an increase in particle size and growth of AuNPs. It can also be inferred that the Au nanoparticles formed on cellulose fibers by the in situ biosynthesis were dispersed on the surface of the fibers, since with a higher dispersion of metal nanoparticles more interactions occur between particles, which contribute to the enhancement of surface plasmon absorption. Previous studies have reported similar effects on particle size and polymodal size distribution depending on the amount of chloroaurate ions involved in nanogold synthesis using plant extracts [38, 39].

The microstructure of UBK-AuNPs composites was characterized by FESEM in BE mode, and images are shown in Figure 3. Due to the distinctive difference in contrast, gold nanoparticles can be readily identified as white dots dispersed over the fibers. The images confirm that gold nanoparticles were successfully formed and decorated the surface of the fibers. As clearly observed in Figure 3(c), gold nanoparticles had a predominately spherical shape with sizes of less than 100 nm in diameter, which was found to be the most common morphology along with sparse rod-shaped and triangular plates. The images distinctly indicate that incremental number and surface coverage of AuNPs on fiber can be achieved simply by varying the concentration of the chloroauric acid solution.

Figure 4 shows XRD patterns of various AuNPs composited fiber sheets and unbleached kraft paper. Unbleached kraft paper exhibited diffraction peaks at 2θ = 17.3°, 23.1°, and 34.9°, which are typical for crystalline cellulose I [40]. By contrast, fiber-AuNPs composite sheets had not only characteristic peaks corresponding to the crystalline cellulose I, but also four sharp peaks at 2θ = 38.6°, 44.9°, 65.0°, and 78.0°, which are indexed to the (111), (200), (220), and (311) planes of the face-centered cubic (fcc) lattice of crystalline Au (JCPDS number 04-0784) [41]. This result suggests that Au nanocrystals were effectively produced while the intrinsic crystalline structure of the cellulose matrix remained intact. It is also evident that as more chloroaurate ions were involved in the preparation, the Au diffraction peaks gradually increased and became sharper, indicating particle growth and an increase in particle size in accordance with gradual sharpness and blue-shift of the surface plasmon absorption as discussed in Figure 2. The average particle size of each fiber-nanogold composite was calculated from the X-ray line broadening, using the Scherrer equation [42] as follows: where is the mean diameter of the particle (nm), λ is the wavelength of the X-ray used, β is the full width of diffraction lines at half of maximum intensity (radians), and is the diffraction angle corresponding to the maximum peak. Based on this formula, average size of AuNP was estimated to be 12.4, 16.4, and 21.0 nm in order of increasing chloroauric acid concentration.

The presence of Au and Au-related compounds on the fibers was also studied by XPS. Survey scan analyses of UBK paper and the UBK-AuNPs composite are presented in Figure 5. As seen in Figure 5, an additional peak corresponding to Au appeared with the as-prepared nanogold composite sheet, which was absent in the unbleached kraft paper spectrum. In addition, it was observed that the ratio of C and O in the final composite slightly increased from 0.48 to 0.5, which may be attributed to the participation of cellulose in gold synthesis and, in part, thermal degradation. Inset in Figure 5 shows the XPS spectrum of the Au 4f region, which can be well fit by two peaks centered at BE positions of 84.1 eV and 87.8 eV assigned to the Au 4f7/2 and Au 4f5/2 core levels of metallic gold (Au0), respectively [43]. No peaks corresponding to Au3+ (85.8 and 89.5 eV) [44] or Au-O species (85.5 eV) [45] were observed. This result is in good agreement with the XRD characterization and provides further evidence that gold ions (Au3+) were successfully reduced to metallic pure Au that bound to the cellulose fibers. The XPS peak for C 1s at BE = 284.6 eV ascribed to adventitious carbon was used to correct the binding energy shift produced by the sample.

Figure 6 shows FTIR spectra of unbleached kraft paper and cellulose fiber-AuNP composite sheets. No distinguishing peaks were observed between samples except those in the region between 1550 and 1650 cm−1, which were assigned to the aromatic skeleton vibration of lignin, conjugated C=O stretching of the phenolic group, and C-O stretching from lignin [46, 47]. In particular, a reduction in the intensity of the peak at 1580 to 1585 cm−1, which is associated with the α-carbonyl group on lignin, is compatible with oxidation of the clustering and movement of Au0 species resulting from Au3+ bioreduction occurring in the electron rich lignin component. This result is indicative of participation of the lignin component in AuNP synthesis. A similar result was reported by Li et al., indicating that the C=O vibration peak changed slightly with a higher concentration of silver ion [48]. Johnston and Nilsson recently reported that nanogold and nanosilver can be formed and bind directly to the surface of paper fibers, and for this synthesis, phenol and aromatic methoxy groups of lignin are essential to reduce Au3+ to Au0 and Ag+ to Ag0, respectively [31].

Figure 7 illustrates the DPPH radical scavenging rate of cellulose fiber-Au nanocomposites under light and dark condition and surface morphology of composite sheets used in this study. UBK was also tested to examine DPPH adsorption and to obtain pure AuNP effect on radical scavenging in UBK-AuNP samples. As seen in Figure 7(a), DPPH adsorbed by UBK and its efficiency was about 47.7% of initial DPPH concentration. In contrast, UBK-Au nanocomposites showed significantly improved DPPH radical scavenging capacity in both the presence and absence of light. Interestingly, when cellulose-AuNP nanocomposite was exposed to light, the scavenging rate (86.05% ± 0.009) was slightly higher than that from the dark condition (77.86% ± 0.006), indicating AuNP becomes more sensitive to quench reactive radicals by light assisted activation [49, 50]. It seems reasonable to assume that adsorption occurred first mostly by fibers and voids in the layered fiber matrix and subsequently contributes to enhancing the AuNP radical scavenging. As seen in the micrographs the fibers formed dense fiber network structures resulting from internally fibrillated and flexible fibers. Compared to UBK sheet, UBK-AuNP composite sheet has a somewhat loose configuration and was found to contain many large pores between fibers. As a result, microscale voids formed from layered fiber network improve the adsorption affinity of DPPH molecules of UBK-AuNP composite. Improved adsorption capacity synergistically contributes to increased antioxidant performance with gold nanoparticles.

4. Conclusions

Cellulose fiber-AuNPs composites have been prepared by a one-step direct synthesis of gold nanoparticles on unbleached softwood cellulose fibers and were investigated for enhanced antioxidant property under ambient condition. It was found that Au nanoparticles were successfully bioreduced to Au0 from Au3+ without external reducing reagents and were identified metallic gold according to XPS scan of Au 4f region. It was further observed that, thorough analyses by UV-Vis DRS, FESEM, and XRD, nanoscaled gold particles were well-conjugated directly onto the fiber surface. Antioxidant activity of AuNP composited fiber in scavenging DPPH solution was much higher than that of pure fiber composites due to the catalytic function of AuNPs and this result poses possible application for the antioxidant food packaging.

Conflict of Interests

The authors declare that there is no conflict of interests regarding the publication of this paper.

Acknowledgments

This study was carried out with the support of “Forest Science and Technology Projects (Project no. S111313L030120)” provided by the Korea Forest Service and the Basic Science Research Program through the National Research Foundation of Korea (NRF) funded by the Ministry of Education (Grant no. 2013R1A1A2060023).