- Nano Express
- Open Access
Highly Efficient Catalysis of Azo Dyes Using Recyclable Silver Nanoparticles Immobilized on Tannic Acid-Grafted Eggshell Membrane
- Xiaojing Liu†1,
- Miao Liang†1,
- Mingyue Liu1,
- Rongxin Su1, 2, 3Email author,
- Mengfan Wang1, 3Email author,
- Wei Qi1, 2, 3 and
- Zhimin He1
© The Author(s). 2016
- Received: 24 April 2016
- Accepted: 20 September 2016
- Published: 1 October 2016
In this study, a facile one-step synthesis of a novel nanocomposite catalytic film was developed based on silver nanoparticles (AgNPs) immobilized in tannic acid-modified eggshell membrane (Tan-ESM). Tannic acid, as a typical plant polyphenol from oak wood, was first grafted onto ESM fibers to serve as both the reductant and the stabilizer during the synthesis of AgNPs. The morphology, constitution, and thermal stability of the resulting AgNPs@Tan-ESM composites were fully characterized to explain the excellent catalytic efficiency of AgNPs@Tan-ESM composites. These composite catalysts were applied to the degradation of azo dyes which exhibited the high catalytic activity toward Congo red and methyl orange according to the kinetic curves. More importantly, they can be easily recovered and reused for many times because of their good stability.
- Azo dyes
- Eggshell membrane
- Tannic acid
- Silver nanoparticles
Today, azo dyes have been extensively applied in the textiles, plastics, foods, drugs, cosmetics, and electronics industries . Due to the toxic nature and poor biodegradability, azo dyes usually give rise to serious environment problems and health hazards during their manufacturing and storage. Thus, more and more attentions have been paid on the elimination of azo dyes through physical-chemical methods, such as biological degradation [2, 3], enzymatic degradation , Fenton-like process [5, 6], photocatalysis , and adsorption tactics [8, 9]. Among these, the biological degradation using anaerobic bacteria is usually suppressed in the presence of oxygen. And enzymatic treatments usually work on a specific type of dyes due to their narrow substrate specificity. Physical methods, such as active carbon adsorption or membrane filtration, usually lead to sludge which increase the operation cost. Photocatalysis seems to be more environmental friendly and energy saving [10, 11], but the practical applications are still limited because their activity are confined in ultraviolet range and the quantum yield is not satisfactory [12, 13].
Over the past few decades, metal nanoparticles have attracted considerable attention owing to their potential applications as catalysts [14–18]. The large surface-to-volume ratio endows metal nanoparticles with high activity. However, the small size brings some inevitable problems in separation and recycling. In order to overcome these problems, many efforts have been carried out to immobilize metal nanoparticles onto solid supports, such as inorganic oxides [19–21], insoluble polymers , hydrogel , and cross-linked protein crystal . However, the synthetic polymer usually needs a complicated preparation process, and the hydrogel is fragile to the intensive agitation during reaction.
Eggshell membrane (ESM) is a kind of double-layered membrane in the inner side of eggshells. With the worldwide increasing consumption of eggs in food industry, a huge amount of eggshells have been thrown away as waste. However, as the bioresource, ESM is made up of more than 80 % proteins and hence has various functional groups. Besides, the intertwined fibrous network is mechanically stable which makes ESM an ideal support material for the immobilization of nanoparticles.
In the previous work, we have found that the physical adsorption on natural ESM is not strong enough to maintain the activity of silver nanoparticles (AgNPs) during reaction and recycling processing . Therefore, it prompts us to develop a method to immobilize AgNPs on modified ESM so as to enhance the stability. Tannic acid, a natural plant polyphenol from oak wood, is considered to be a “green” reagent in the synthesis and immobilizing of AgNPs because the silver ions can be reduced by the phenolic hydroxyls under a mild condition without any other reducing agents.
Therefore, in the present work, a facile synthesis method was developed to immobilize AgNPs by grafting tannic acid onto the eggshell membrane (Tan-ESM) and in situ reducing silver ions without additional reductant. By this way, a stable linkage between AgNPs and ESM can be constructed to form the AgNPs@Tan-ESM composites. The physical and chemical properties of AgNPs@Tan-ESM composites were fully characterized. Finally, Congo red (CR) and methyl orange (MO) were chosen as the model substrates to investigate the catalytic behaviors of AgNPs@Tan-ESM composites in the degradation of azo dyes.
Fresh eggshells were collected from local market. Tannic acid (>98 %) was purchased from Guangfu Fine Chemical Research Institution (Tianjin, China). Glutaraldehyde (50 wt.%), silver nitrate (AgNO3, >99 %), sodium borohydride (NaBH4, >98 %), CR (>97 %), and MO (96 %) were purchased from Aladdin Reagent Co. (Shanghai, China). The ultrapure water (>18 MΩ cm) that prepared from a three-stage Millipore Milli-Q Plus 185 purification water system (Millipore Corp, Bedford, USA) was used throughout all the experiments.
Preparation of Tan-ESM
ESM was carefully torn off from the inner side of fresh eggshell, cleaned with deionized water to remove the residual albumen, and stored in deionized water at 4 °C. In a typical procedure, ESM was cut into small pieces (5 mm × 5 mm) and vacuum dried at room temperature. Then, 0.5 g of dried ESM pieces was dispersed into 50.0-mL deionized water containing a certain amount of tannic acid under the continuous stirring at 37 °C. After 2 h, 0.75-mL glutaraldehyde was added into the mixture; the reaction was kept stirring for 6 h at 37 °C until the color of ESM turned yellow. The obtained Tan-ESM pieces were separated and washed with deionized water for several times to remove the unreacted tannic acid. Finally, Tan-ESM was vacuum dried at room temperature and ready for the following experiments.
Preparation of AgNPs@Tan-ESM Composites
The as-prepared dried Tan-ESM pieces were dispersed into 50.0 mL AgNO3 solution (10 mM) and stirred at 37 °C. After 12 h, the obtained AgNPs@Tan-ESM composites were separated, washed with deionized water, and vacuum dried.
Degradation of Azo Dyes Catalyzed by AgNPs@Tan-ESM
In a typical catalytic experiment, 11 mg of AgNPs@Tan-ESM composites was dispersed into a freshly prepared solution containing 8 mL deionized water and 500 μL CR or MO solution (3 mM). N2 was piped into the solution for 10 min to remove the dissolved oxygen. After the preheating at 40 °C, 0.9 mL of NaBH4 solution (0.3 mM) was rapidly injected into this mixture to start the reaction. The reaction was monitored by UV-vis absorption spectra (Persee TU-1810, China) in the range of 250–700 nm through withdrawing samples from reaction mixture at each time interval.
The surface morphologies of natural ESM, Tan-ESM, and AgNPs@Tan-ESM composites were characterized by scanning electron microscopy (SEM; S-4800, Hitachi Ltd.) at an accelerating voltage of 3.0 kV equipped with an energy-dispersive X-ray (EDX). All samples were vacuum dried before determination. The morphology of the AgNPs was characterized by a high-resolution transmission electron microscopy (HRTEM, JEM-2100 F, 200 kV). A sufficient dispersed AgNP sample was obtained through high-intensive ultrasonic treatment of AgNPs@Tan-ESM composites in water. Then, a droplet of dispersions was dropped on a carbon-coated copper grid and dried at room temperature. The X-ray diffract (XRD) pattern were collected on an X-ray diffract meter (D/max 2500, Rigaku) with a Cu Kα radiation. The thermogravimetric analysis (TGA) of natural ESM, Tan-ESM, and AgNPs@Tan-ESM composites were carried out on a simultaneous TGA-DTA apparatus (PTC-10A, Rigaku, Japan) through gradually heating the samples from the room temperature to 700 °C at the rate of 10 °C/min. The attenuated total reflectance fast Fourier transformation infrared (ATR-FTIR, Nicolet Nexus 670) spectrum from 4000 to 400 cm−1 was collected to analyze the functional groups of the samples.
Preparation of AgNPs@Tan-ESM Composites
Characterization of AgNPs@Tan-ESM Composites
As a typical plant polyphenol, tannic acid is rich in orthophenolic hydroxyl groups which make it a preeminent ligand to chelate Ag ions and form the stable five-member chelating rings . Compared with procyanidine that reported in our previous work , tannic acid provides more binding sites for metal nanoparticles. Due to the reducing capacity of orthophenolic hydroxyls in tannic acid, the Ag ions can be spontaneously reduced to Ag0 atoms without adding other reducing agents. With the in situ nucleation and growth, Ag0 formed AgNPs and could be stabilized through interacting with the oxygen atoms on tannic acid molecules. Therefore, the color of ESM was found turning from yellow to deep brown, confirming the formation of AgNPs@Tan-ESM composites.
The network structure of ESM provides a large specific surface area for AgNPs to nucleate and grow. As shown in Fig. 1e, f, the network structure was remained after the reduction reaction and lots of nanoparticles were found decorated on the fiber surface which make the fiber surface even rougher. Therefore, it is believed that ESM is a robust biomatrix for the immobilization of nanoparticles. The prominent reducibility of tannic acid and the excellent stability of ESM facilitate the fabrication of AgNPs@Tan-ESM composites.
Comparing with natural ESM, several new peaks appeared in the spectra of Tan-ESM and AgNPs@Tan-ESM composites. The peaks at 1716 and 1319 cm−1 reflect the form of Ar–COOR, the peak at 1033 cm−1 corresponds to the C–O–C stretching vibration of the benzene ring, and the peak at 1195 cm−1 owes to the C–O–H stretching vibration of phenolic hydroxyls. Besides, the characteristic peaks of long-chain alkane at 758–721 cm−1 reflect the existence of glutaraldehyde. All these results indicated that the tannic acid has been successfully grafted on the surface of the ESM. Comparing with Tan-ESM, the transmittance of AgNPs@Tan-ESM composites was slightly depressed around 3300 cm−1, indicating the interactions between Tan-ESM and AgNPs.
Furthermore, TGA was performed to investigate the thermal stability of natural ESM, Tan-ESM, and AgNPs@Tan-ESM composites as shown in Fig. 4b. All the samples were gradually heated from room temperature to 700 °C at the rate of 10 °C/min. Due to the releasing of the bound water, the weight of all the samples decreased slowly before 250 °C. Beyond 250 °C, the weight began to drop sharply which demonstrated the drastic decompose of ESM until 570 °C. The identical TGA curves of ESM, Tan-ESM, and AgNPs@Tan-ESM composites imply their similar thermal stability. Based on the TGA curve, the AgNP content in AgNPs@Tan-ESM composite can be approximately calculated as 3.3 %. It is almost twice the content of AgNPs on AgNPs@ESM composites (1.64 %) which immobilized AgNPs on the plain ESM through physical absorption .
Catalytic Degradation of Azo Dyes
Azo dyes are the most important synthetic colorants which have been widely used in textile, printing, paper manufacturing, etc. However, azo dyes can be easily broken down to aromatic amine, which leads to a serious risk to environment. In this study, CR and MO were chosen as the typical reaction substrate to evaluate the catalytic ability of AgNPs@Tan-ESM composites in the degradation of azo dyes.
where r CR and r MO are the consumption rates of CR and MO at a certain time of t, C CR and C MO are the concentrations of CR and MO at t, and k CR and k MO are the reaction rate constants.
Figure 5b, d shows the kinetic curves for the degradation of CR and MO. Linear relationship between ln(Ct/C0) and reaction time suggested that the degradation reaction abides by the pseudo-first-order kinetics model, and the rate constants for CR (k CR = 0.299 min−1) and MO (k MO = 0.090 min−1) can be calculated as described in supporting materials. Comparing with the AgNPs immobilized on silica (k MO = 0.035 min−1) , the synthesis AgNPs@Tan-ESM composites displayed excellent catalytic activity in the degradation of MO at a low molar ratio of NaBH4 to dyes. This is because the network structure of ESM contributes to the forming of small size AgNPs and the high loading of AgNPs.
Catalyst Stability and Reuse
In this study, tannic acid was firstly grafted onto ESM so as to in situ reduce Ag ions into AgNPs and subsequently immobilize the formed AgNPs onto the surface of ESM. As a catalyst, the resulting AgNPs@Tan-ESM composites exhibited excellent catalytic activity for the degradation of azo dyes in aqueous phase. Moreover, due to the stability of ESM, AgNPs@Tan-ESM composites can be easily recovered and reused at a high catalytic efficiency. By combing the merits of tannic acid and ESM, a novel strategy was presented to obtain an environmental friendly, simple, and effective catalyst for the environmental treatment of azo dyes.
The authors gratefully acknowledge the financial support from the Natural Science Foundation of China (51473115 and 21206113), the Ministry of Science and Technology of China (2012YQ090194), and the Natural Science Foundation of Tianjin (16JCZDJC37900).
XJL and RXS designed the research; XJL and ML performed the research; all the authors analyzed the data and wrote the paper. All authors read and approved the final manuscript.
The authors declare that they have no competing interests.
Open AccessThis article is distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution, and reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made.
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