Mengmeng Zhang,
Xuan Lu,
Hao-Yi Wang,
Xiaoli Liu,
Yujun Qin*,
Pu Zhang and
Zhi-Xin Guo
Department of Chemistry, Renmin University of China, Beijing 100872, China. E-mail: yjqin@ruc.edu.cn
First published on 4th April 2016
We report the in situ reduction and incorporation of gold nanoparticles into graphene oxide/polyethyleneimine composites with polyethyleneimine acting as the reducing and protecting agent for the gold nanoparticles. The resulting composites with porous structure are obtained through a simple freeze-drying method with the gold nanoparticles uniformly distributed on the graphene oxide sheets. The morphology and composition of the composite are characterized by scanning electron microscopy, transmission electron microscopy, X-ray photoelectron spectroscopy, X-ray diffraction and Raman spectroscopy. The catalytic test indicates that the as-prepared porous gold nanoparticle-embedded composite catalyst could efficiently activate the reduction of 4-nitrophenol to 4-aminophenol. The recycling measurement reveals that the activity of the recovered catalyst decreases a little, mainly due to the restacking of the graphene sheets. Moreover, the porous composites used as packing material in chromatography column and injection syringe exhibit good catalytic performances in the rapid reduction of 4-nitrophenol, implying the potential applications of such porous heterogeneous catalysts in continuous catalytic reaction.
The utilization of porous graphene materials as support of metal catalyst is also an attractive research field.22 Compared with the traditional catalyst supports, the high specific surface areas of graphene could provide more anchoring sites for the catalyst, impeding the aggregation of the metal nanoparticles. GO is often used as the support instead of graphene because the organic groups of GO make it possible to bring new surface functionalities or assemble with other components, which could enhance the interactions with the anchored metal nanoparticles. The ab initio calculations suggest that GO is a much better support candidate of metal nanocatalysts than graphene in terms of activity and feasibility.23 Moreover, the hydrophilic property of GO would favor the transport of reactants through graphene network and facilitate their contact with metal nanoparticles in aqueous reactions. Many metal nanoparticles, including gold, silver, platinum, palladium and copper, have been deposited on graphene or GO and demonstrated superior catalytic performances.24–28 Wang et al. have incorporated different noble metal nanoparticles into graphene aerogels through the hydrothermal method, which showed high catalytic activity and selectivity in the organic reaction.27 Jiao et al. have fabricated graphene-based hydrogel from the in situ co-reduction of GO and silver acetate for the efficient photocatalytic degradation of organic dyes.29 In a general strategy, GO is simultaneously reduced to rGO with the reduction of metal salt precursor, and the resulting rGO sheets assemble into robust graphene matrix within which the metal nanoparticles are uniformly deposited.
However, the catalytic performance of the porous graphene-nanoparticles composites with fixed/definite shapes is somewhat limited for they could not be distributed in the reaction solution, although the recycle is easy. The good dispersion of the catalyst in the reaction system could facilitate the contact of reactants with catalysts, leading to the improvement of the catalytic efficiency. In this work, we report the preparation of gold nanoparticles loaded on porous composites of polyethyleneimine (PEI) and GO through the in situ reduction and deposition of gold nanoparticles and a simple freeze-drying process. The resulting porous functional composite exhibits excellent catalytic activity for the reduction of 4-nitrophenol. Moreover, the chromatographic column or injector syringe packed with the as-prepared composite demonstrates superior continuous catalytic performance.
The composite of gold nanoparticles and GO was prepared as follows. 20 mg of GO was dispersed in 10 mL of water and the pH value of the dispersion was adjusted to 10 with ammonium hydroxide before 1 h of ultrasonication. Then the mixture of 1 mL of PEI solution (10 mg mL−1) and 0.5 mL of HAuCl4·4H2O solution (20 mg mL−1) was added to the GO dispersion under vigorous stirring. The mixture was stirred for 2 h before moved to an oil bath at 80 °C and stirred for another 1 h. At last, the product was cooled to room temperature in air and treated by a freeze-dryer to obtain Au/PEI/GO composite powder of 35 mg. For comparison, the composite film was prepared as the procedure above, only replacing the freeze-drying method with the vacuum-filtering method.
To test the catalytic activity of the composites, 15 mL of aqueous 4-nitrophenol solution (0.1 mM) and 15 mL of freshly prepared aqueous NaBH4 solution (0.2 M) were mixed at room temperature. Then 5 mg of Au/PEI/GO powder was added into the stirred solution to catalyze the transformation of 4-nitrophenol to 4-aminophenol, which was monitored by UV-vis absorption spectrophotometer in the reaction process. At the end of the reaction, the catalyst was collected by filtering, washed thoroughly with water for the next cycle.
For the continuous catalytic test, Au/PEI/GO composite powder was packed in a thin glass chromatographic column or an injector syringe, with cotton wools placed at the bottom and top of the powders. The mixture solution of NaBH4 and 4-nitrophenol was added in the column or syringe from the top and flowed through the Au/PEI/GO packing. The effluent was collected in a vial.
Scanning electron microscopic (SEM) characterization was conducted on a JEOL JSM-7401F at an accelerating voltage of 5 kV. Transmission electron microscopic (TEM) images were captured on a JEOL 2010 operating at an accelerating voltage of 200 kV through a Gatan model 780 CCD camera. X-ray diffraction (XRD) analysis was obtained on Shimadzu XRD-7000 using Cu Kα radiation in the 2θ range from 2° to 80° with a scan rate of 2° min−1. X-ray photoelectron spectroscopy (XPS) was carried out on a Kratos AXIS Ultra using 300 W Al Kα radiation. Raman spectra were recorded with a Horiba XploRA PLUS confocal microscope using 532 nm laser excitation. Fourier transform infrared (FT-IR) spectra were collected on a Bruker Tensor 27 instrument. Thermogravimetric analysis (TGA) measurement was performed on a Q50 TA instrument and the samples were analyzed in platinum pans from room temperature to 700 °C under steady nitrogen at a heating rate of 5 °C min−1. UV-vis absorption measurement was conducted on a Shimadzu UV-3600 spectrometer.
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| Fig. 1 Photograph (a) and SEM images at low (b) and high (c) magnification of Au/PEI/GO composites from freeze-drying. | ||
The detailed chemical signatures of Au/PEI/GO composite obtained from SEM-EDX (Fig. S2†) also confirm the presence of Au, as well as other elements in the composite. Calculated from the initial recipe and the resulting weight of the product, the content of gold in the Au/PEI/GO composite is 13.6%, close to the value of 12.2% estimated from the TGA results (Fig. S3†). It is notable that although the as-prepared porous composite in our case is fragile with relatively poor mechanical strength, the superior dispersibility in solvent would facilitate their application in the subsequent catalysis reaction.
Further investigation of the gold nanoparticles is conducted on TEM, as seen in Fig. 2a, where a large number of gold nanoparticles are uniformly loaded on graphene sheet without aggregation. The size distribution exhibits that the diameters of the nanoparticles are mainly in the size range 4–18 nm, and the mean particle diameter is about 9.8 nm (Fig. 2b). The selected area electron diffraction (SAED) shows sharp reflexes of ordered regions of Au (Fig. 2c). In addition, the regular d-spacing of Au nanoparticle observed in the high resolution TEM image (Fig. 2d) is well matched with the (111) planes of crystalline gold.34
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| Fig. 2 (a) TEM image of Au/PEI/GO composite, (b) size distribution of gold nanoparticles, (c) SAED pattern for the ordered regions of gold and (d) high resolution TEM image of a gold nanoparticle. | ||
XPS is also used to detect the compositions of the samples. The survey XPS spectra of Au/PEI/GO composites and GO are shown in Fig. 3a. Obviously, the characteristic peaks of C 1s and O 1s are observed at 285 and 532 eV, respectively, for both the samples, while three new peaks assigned to N 1s, Cl 2p and Au 4f, respectively, are observed for the composite. The N 1s peak at 399 eV is assigned to the presence of PEI and the Cl 2p at 197 eV is attributed to the byproduct from chloroauric acid. The existence of Au is confirmed by the Au 4f peak around 86 eV, which is zoomed in as Fig. 3b. The diffused peaks with binding energies of 84.0 and 87.5 eV accord well with Au 4f7/2 and Au 4f5/2 in the metallic state, respectively. Fig. 3c and d illustrate the deconvoluted C 1s peaks of Au/PEI/GO and GO, respectively. The peak centered at the binding energy of 284.7 eV is attributed to the C
C bond. The other deconvoluted peaks located at 286.1, 287.0 and 288.6 eV are assigned to the C–OH, C–O–C and C
O respectively.35 Obviously, the relative intensity of the peak associated with oxygen-containing bonds significantly decreases for the Au/PEI/GO sample compared with that of GO, indicating that GO in the composite is partially reduced.36 FT-IR spectrum of GO shows the feature peaks at 1725 and 1627 cm−1 assigned to C
O and C
C stretching, respectively (Fig. S4†). While for the Au/PEI/GO composite, the C
O peak almost disappears, indicating the strong interaction between the carboxylic groups of GO and the amines group of PEI.37
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| Fig. 3 XPS spectra of Au/PEI/GO and GO samples (a) and deconvoluted XPS peaks for (b) Au 4f of Au/PEI/GO, (c) C 1s of Au/PEI/GO and (d) C 1s of GO. | ||
To further characterize the structure of Au/PEI/GO composite, its XRD spectrum is measured and shown in Fig. 4a. The peaks at 38.35°, 44.54°, 64.81° and 77.71° are assigned to face-centered cubic bulk Au (111), (200), (220) and (311), respectively, which are in agreement with the standard values of gold (JCPDS 04-0784)38 and the SAED patterns (Fig. 2c). The spectrum also displays the characteristic peak of GO at 9.8°, lower than the peak of GO at 11.2°, indicating the increase of the interlayer spacing of GO in the composite compared with the original GO.37 The XRD pattern of the film composite from vacuum-filtering shows two obvious peaks at 12.8° and 24.2° (Fig. S5†), which suggests the existence of different GO sheet assembly in the sample. The former peak corresponding to the d-spacing of 0.69 nm implies the intercalation of PEI into the GO layers.39 While for the peak at 24.2° with the d-spacing of 0.37 nm, a little higher than that of 0.34 nm for graphite, it could be ascribed to the tight stacking of GO owing to the vacuum-filtering and the π–π interaction of the partially reduced GO.
The Raman spectra of Au/PEI/GO and GO exhibit two peaks at 1335 cm−1 and 1589 cm−1 corresponding to the D and G bands, respectively (Fig. 4b). The G band is assigned to the first-order scattering of the E2g mode observed for sp2 carbon domains and the D band is associated with disordered structural defects. The intensity ratio between the D and G bands (ID/IG) can be used to estimate the degree of structural disorder. In our case, the ID/IG value is 1.32 for the Au/PEI/GO sample, much high than the GO value of 0.91, which could be ascribed to the interaction of PEI with GO and the partial reduction of GO.40,41
The catalytic performance of the Au/PEI/GO composite is studied by the reduction of 4-nitrophenol to 4-aminophenol with NaBH4, a representative reaction to evaluate the catalytic activity of gold nanoparticles.42–44 The reduction process could be easily monitored by UV-vis spectra because of the feature absorption at 400 nm and 300 nm for 4-nitrophenol and 4-aminophenol, respectively. Before the addition of the catalyst, the yellow-green mixture solution of 4-nitrophenol and NaBH4 shows a strong peak assigned to the nitro group at 400 nm in UV-vis spectrum. Upon the adding of the catalyst, the reduction reaction is activated and the peak at 400 nm begins to decrease. At the same time, a new peak at 300 nm owing to 4-aminophenol appears and grows. Fig. 5a clearly illustrates the evolution of UV-vis spectra recording the transforming of 4-nitrophenol to 4-aminophenol in the reaction procedure, with the decrease of the peak at 400 nm and the development of the peak at 300 nm. When the reaction finishes after 7 min, the peak at 400 nm almost disappears and the solution becomes colorless, implying the complete reduction of the initial nitro compound. Fig. 5b shows the variation of ln
A (A is the absorbance value at 400 nm from Fig. 5a) with the reaction time, which could be fitted as a linear correlation, indicating that the reduction reaction obeys the pseudo-first-order kinetics. The rate constant (K) obtained from the slope of the fitting straight line is 9.87 × 10−3 s−1. The ratio of constant K over the catalyst weight (k = K/m) is 1.97 s−1 g−1, much higher than the reported ratio of spongy gold nanocrystals45 and similar to the carbon nanotube/GO composite supported gold nanoparticles.46 The catalytic performance of composite for vacuum-filtering is also measured after grinding, which presents the k value of 0.85 s−1 g−1, much lower than that of the porous sample.
The reusability is an important feature for the evaluation of heterogeneous catalyst. Herein, the Au/PEI/GO composites are recycled and used in a new reaction to test the catalytic activity for 4 time, and the corresponding K values is shown in Fig. 5b inset. Obviously, the K value decreases about 10% after each cycle, which might partially be attributed to the sample loss in the recycling process involving filtering and washing. However, the structure of the composite after reaction, which would significantly influence the recycling catalytic behavior, should be further investigated.
The morphology of the Au/PEI/GO composite after 4 catalytic cycles is observed by SEM. As shown in Fig. 6a, the porous structure of the composite is relatively well kept, while the graphene sheets present the tendency of wrinkling and aggregating. The shrinking of the composite would lead to the restacking of GO sheets and harm the catalytic activity of gold nanoparticles. The magnified image shown in Fig. 6b reveals that the gold nanoparticles on the GO sheet still maintain a good distribution without obvious change after the reaction cycles, compared with Fig. 1c, which ensures the relatively high catalytic performances of the recycled sample. The XRD pattern of the recovered composite catalyst clearly presents the existence of Au, while the pronounced peak at 21.6°, corresponding to the layer spacing of 0.41 nm, indicates the restacking of the GO layer.39
Although the catalytic activity decreases in the recycling test owing to the stacking of the GO sheets. The advantage of the porous composite catalyst is the good dispersion in the reaction system, which could improve the contacts of the gold nanoparticle with the reactants. In fact, a possible application of this kind of powder catalyst is chromatographic packing material.47 Fig. 6d shows the photograph of a chromatographic column packed with the Au/PEI/GO composite. The continuous reduction of 4-aminophenol could be realized in the column with good efficiency, indicating the possibility of large-scale use in fixed- or fluid-bed catalysis processes.27 For better demonstration of the design, the Au/PEI/GO composite is packed in an injector and the yellow-green solution of 4-nitrophenol and NaBH4 is pushed through the catalyst packing layer in a few seconds (Fig. 6e). The colorless effluent received in vial indicates the high efficiency of the reduction from 4-nitrophenol to 4-aminophenol (also see in Video S,† with the speed of ∼0.8 mL s−1 for the liquid passing through the catalyst).
Footnote |
| † Electronic supplementary information (ESI) available: The characterization of EDX, TGA, FT-IR for porous Au/PEI/GO composite and SEM, XRD for Au/PEI/GO composite from vacuum-filtering. See DOI: 10.1039/c6ra01772j |
| This journal is © The Royal Society of Chemistry 2016 |