1. Introduction
Natural enzymes have attracted much attention because of their high catalytic efficiency and strong response characteristics. However, natural enzymes have many problems such as inactivation and denaturation, difficulty in purification, high cost and difficulty in storage and easily affected by environmental conditions including pH, temperature and inhibitors [1] [2]. These defects largely limit the application of enzyme. Therefore, the preparation and application of artificial mimic enzymes is a current research topic in recent years. In the past few decades, many mimic enzymes have been discovered [3] [4], for example, cytochrome P450 mimetics [5], serine proteases mimetics [6], dioxygenase mimetics [7], phosphodiesterase mimetics [8] and so on. Among these, a large number of peroxidase mimics, such as hemin [9] [10], hemeatin [11], hemoglobin [12], cyclodextrin [13], and porphyrin [14] [15], etc, have been used for H2O2 and ascorbic acid detection [13] [14]. However, these peroxide mimic enzymes have lower catalytic activity and poorer selectivity than natural enzymes. Therefore, it is necessary to work harder to design a mimetic enzyme with high catalytic activity.
Metal-organic frameworks (MOFs) are topologically formed by organic ligands and inorganic metal clusters, a type of zeolite-like crystalline porous materials, have been recently researched as new functional materials. Compared with traditional zeolite, activated carbon and other materials, it has the advantages of high specific surface area, adjustable pore structure and easy modification. It has extensively application prospects in the fields of gas storage [16], separation [17] and catalysis [18], and has attracted much attention in science and biological systems. In view of the above advantages of MOFs, we consider it to be a material suitable for simulating enzymes. Indeed, Fe-MIL-101 [19], Fe-MIL-88NH2 [20], MIL-53(Fe) [21], MIL-100(Fe) and MIL-68(Fe) [22] were found to have the activity of peroxide mimicking enzyme. Cu-MOF [23] was synthesized for catalyzing hydrolysis of bovine serum albumin and casein by solvothermal method. Despite the many exciting and convincing developments recently, we believe that the MOF-based catalytic field is still in the development and immature stage. In this work, we make use of the novel properties of 5% Fe/Fe-MIL-101 as peroxidase mimetics to catalyze oxidation of the ABTS by H2O2.
2. Methods
2.1. Chemicals and Instrumentation
All commercial chemicals were used without further purification. Terephthalic acid (H2BDC, 99%), Ferric chloride hexahydrat (FeCl3・6H2O, 99%), ethanol (99.5%), sodium borohydride (NaBH4), NaOH, hydrogen peroxide (H2O2) were purchased from Sigma-Aldrich. 2,2’-azino-bis(3-ethylbenzothiazoline-6-sulfonicacid) diammonium salt (ABTS) were obtained from BBI (Ontario,Canada). X-ray powder diffraction (XRD) experiments were conducted on a D/max-3B spectrometer with Cu Kα radiation. Scans were made in the 2θ range 3˚ - 40˚ with a scan rate of 10˚ min−1 (wide angle diffraction). Scanning electron microscopy (SEM) images of samples were obtained with a FEI Quanta 200FEG microscope. BET surface areas and pore volumes were measured through nitrogen adsorption/desorption measurements using a Micromeritics Tristar II surface area and porosity analyzer.
2.2. Synthesis of Fe/Fe-MIL-101
The Fe-MIL-101 is synthesized by hydrothermal method using p-dibenzoic acid as ligand iron as metal active center [24]. FeCl3・6H2O (0.675 g) was added slowly into DMF (15 mL) solution, followed by adding H2BDC (0.206 g). The mixture was under continuous mechanical stirring for 10 min at room temperature, and then transferred into a Teon-lined stainless steel autoclave and heated at 110˚C for 20 h. The resulting brown solid was separated from the reaction medium, and purified by using the hot ethanol (70˚C), the purification process was carried out several times, followed by drying in an oven (70˚C, 30 min). The particles were separated by centrifuging and washed with DMF and ethanol to remove any unreacted raw materials.
2.3. Preparation of 1% Fe/Fe-MIL-101
FeCl3・6H2O (0.0195 g) and Fe-MIL-101 (0.4 g) were dissolved in ethanol, stirred at room temperature for 1 h, centrifuged and washed 3 times in ethanol and dried under vacuum at 80˚C to obtain the product 1. NaBH4 (2 mL, 1.875 mg/mL) solution was added dropwise to the solution of product 1 (product 1:150 mg, ethanol: 10 mL, dichloromethane: 50 mL), stirred at 0˚C under nitrogen for 30 min and then stirred at room temperature for 30 min. The precipitate was collected by centrifuging to obtain the product 1% Fe/Fe-MIL-101.
3% Fe/Fe-MIL-101, 5% Fe/Fe-MIL-101, and 8% Fe/Fe-MIL-101 were prepared by changing the amount of FeCl3・6H2O added.
2.4. Peroxidase-Like Activity of 5% Fe/Fe-MIL-101
The effect of pH, temperature, H2O2 concentration and ABTS concentration on the peroxidase-like activity of 5% Fe/Fe-MIL-101 was performed in a reaction volume of 3 mL of buffer solution. Buffers used in this experiment were acetate buffer (pH 4.0-6.0) and borate buffer (pH 8.0-10.0). The steady state kinetic assays of 5% Fe/Fe-MIL-101 were carried out by changing the concentration of ABTS at a fixed concentration of H2O2 or vice versa at 50˚C. After 5 minutes of reaction, the absorbance of the reaction solution was measured at a wavelength of 420 nm using a Shi-madzu UV-2450 spectrophotometer. The kinetic parameters were calculated based on the equation:
(1)
where ν is the initial velocity, Vmax is the maximal velocity, [S] is the concentration of the substrate, and Km is the Michaelis constant.
3. Results and Discussion
3.1. The Characterization of Fe/Fe-MIL-101
The X-ray diffraction (XRD) pattern of the as-synthesized Fe-MIL-101 is shown in Figure 1(a). The diffraction peaks all corresponded to the products synthesized in the literature [24] and generally consistent with the pattern calculated from the crystallographic data in this reference. Moreover the diffraction peaks position of obtained Fe/Fe-MIL-101 by different iron loadings are the same as Fe-MIL-101, but the intensity of the diffraction peaks are weaker than
Figure 1. (a) XRD patterns of the Fe-MIL-101 and Fe/Fe-MIL-101. (b) N2 adsorption/desorption isotherm pore distribution of 5% Fe/Fe-MIL-101 and Fe-MIL-101.
Fe-MIL-101. The adsorption?desorption isotherms of 5% Fe/Fe-MIL-101 are of type I (Figure 1(b)), indicating the presence of a microporous network. Compared with Fe-MIL-101, the BET specific surface area of the experimentally synthesized 5% Fe/Fe-MIL-101 material decreased from 2737 m2/g to 2148 m2/g, and the pore volume decreased from 0.75 cm3・g−1 to 0.51 cm3・g−1, the average pore size decreased from 2.51 nm to 2.35 nm, the reduction of specific surface area, pore size and pore volume probably due to the blockage of material pores by the loaded iron. SEM images show that 5% Fe/Fe-MIL-101 has a typical octahedron morphology like Fe-MIL-101 (Figure 2(a) and Figure 2(b)), but the surface is rough, and it is obvious that there are small solid iron particles on the surface. All of the results mentioned above confirmed that 5% Fe/Fe-MIL-101 was successfully synthesized.
3.2. Peroxidase-Like Activity of 1% Fe/Fe-MIL-101
In order to study the peroxidase-like activity of 1% Fe/Fe-MIL-101, the conventional catalytic oxidation of the peroxidase substrate ABTS in the presence of H2O2 was tested. As shown in Figure 3, in the absence and presence of H2O2, which displayed a negligible absorption at the maximum absorbance of 420 nm, indicating that ABTS could not be oxidized by H2O2 without any catalysts. In contrast, 1%Fe/Fe-MIL-101 could catalyze the oxidation of ABTS by H2O2 (Figure 3), with a maximum absorbance at 420 nm, indicating that 1% Fe/Fe-MIL-10 gave higher response and showed catalytic activity toward ABTS oxidation in the presence of H2O2.
Table 1 mainly compares the absorbance values of Fe/Fe-MIL-101 with iron loadings at load ratios R = 0.01, R = 0.03 and R = 0.05, R = 0.08, respectively. A significant effect of the load ratio on the absorbance values is visible, the absorbance value are growing with increasing load ratio (R = 0.01 - 0.05), however, the absorbance value is decreasing when the load ratio is increased to 0.08. Since the absorbance value of 5% Fe/Fe-MIL-101 was the largest, 5% Fe/Fe-MIL-101 was selected as the experimental object in the next experiment.
The peroxidase-like catalytic activity of 5% Fe/Fe-MIL-101 was studied by
Figure 2. (a) SEM images of the 5% Fe/Fe-MIL-101 and (b) Fe-MIL-101.
Figure 3. Time-dependent absorbance changes at 420 nm in the presence of (1) H2O2 and ABTS, (2) ABTS and 1% Fe/Fe-MIL-101, (3) H2O2 and ABTS and 1% Fe/Fe-MIL-101.
Table 1. Comparison of absorbance values of different catalyst.
selecting the substrates ABTS and H2O2 as a model reaction system. The peroxidase-like activity of 5% Fe/Fe-MIL-101 was measured at different pH (3.0-9.0) and various temperature (30˚C - 50˚C) (Figure 4(a) and Figure 4(b)). As can be seen from Figure 5, the pH 4.0 and 45˚C were the optimal reaction condition, which are very similar to the values for HRP [25].
3.3. Kinetic Analysis
We used steady-state kinetics to further study the peroxidase-like catalytic mechanism and kinetic parameters of 5% Fe/Fe-MIL-101. The kinetic data was collected by changing the concentration of one substrate at a fixed concentration of the other substrate. Within the concentration range of TMB and H2O2 used,
Figure 4. The peroxidase-like activity of the 5% Fe/Fe-MIL-101 hybrid is dependent on the temperature (a) and pH (b).
Figure 5. ((a) and (c)) Steady-state kinetic assays of 5% Fe/Fe-MIL-101. (a) The concentration of TMB was fixed and the H2O2 concentration was varied in acetate buffer at pH 4.0 (b) double-reciprocal plots of the activity of 5% Fe/Fe-MIL-101. (c) The concentration of H2O2 was fixed and the ABTS concentration was varied in acetate buffer at pH 4.0. (d) double-reciprocal plots of the activity of 5% Fe/Fe-MIL-101.
typical Michaelis-Menten curves were observed (Figure 5). A Lineweaver-Burk plot can be obtained with a nearly linear relationship (Figure 5(b) and Figure 5(d)), from which important kinetic parameters can be derived (Table 2). The kinetic parameters, such as the Michaelis-Menten constant (Km) and maximum initial velocity (Vmax) were from a Lineweaver-Burk plot. The Michaelis constant, Km, the smaller the Km value, the stronger the affinity of the enzyme to the substrate, and the higher the catalytic activity of the enzyme. As shown in Table 2, the Km value of 5% Fe/Fe-MIL-101 (0.095 mM) with ABTS as the substrate under the optimum conditions (20 mM acetate buffer, pH 4.0) was about 3-fold
Table 2. Comparison of the Michaelis constant (Km) of 5% Fe/Fe-MIL-101 and other enzyme mimics at pH 4.0.
lower than HRP (0.319 mM) , and this value is about 108 times less than that of CuO NPs (Km = 10.28 mM) and about 10-fold lower than Fe-MIL-101 (0.916 mM), indicating a much higher affinity for H2O2 than HRP and most of the peroxidase mimetics at pH 4.0.
4. Conclusion
The present study demonstrates that the 5% Fe/Fe-MIL-101 exhibited excellent peroxidase-like activity, catalyzing the oxidation of ABTS in the presence of H2O2. The Michaelis constant (Km) of 5% Fe/Fe-MIL-101 with ABTS as the substrate is about 10-fold smaller than Fe-MIL-101 and about 3-fold smaller than HRP, and about 108 times less than that of CuO NPs (Km = 10.28 mM), indicating a much higher affinity for ABTS than HRP and most of the peroxidase mimetics. The above findings will open such catalytic systems for a variety of potential applications in biological systems in the future because of their ease of preparation, high activity and stability.
Acknowledgements
The authors thank the National Natural Science Foundation of China (81860532) and Key Research and Development Plan of Yunnan Province (2018BA065). The authors also thank the Industrialization Cultivation Project (2016CYH04), Scientific Research Fund of Department of Yunnan Education (2017ZZX223), the Program for Innovation Team of Yunnan Province and Key Laboratory of Advanced Materials for Wastewater Treatment of Kunming for financial support. The authors also thank Research Funding of Yunnan Provincial Department of Transportation (2017-438) and Yunnan Water Conservancy Science and Technology Plan of the Water Resources Department of Yunnan province and the Program for Science and Technology Projects of Yunnan Industrial of China Tobacco Industry CO., Ltd. (2015CP03, 2017539200370194, 2016539200340108) for financial support.