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International Journal of Photoenergy
Volume 2012 (2012), Article ID 598713, 4 pages
http://dx.doi.org/10.1155/2012/598713
Research Article

Synthesis, Characterization, and Evaluation of Boron-Doped Iron Oxides for the Photocatalytic Degradation of Atrazine under Visible Light

Laboratory of Plant Nutrition and Ecological Environment Research, Centre for Microelement Research of Huazhong Agricultural University, Key Laboratory of Subtropical Agriculture and Environment, Ministry of Agriculture, Wuhan 430070, China

Received 23 July 2011; Accepted 15 September 2011

Academic Editor: Shifu Chen

Copyright © 2012 Shan Hu et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

Abstract

Photocatalytic degradation of atrazine by boron-doped iron oxides under visible light irradiation was investigated. In this work, boron-doped goethite and hematite were successfully prepared by sol-gel method with trimethylborate as boron precursor. The powders were characterized by XRD, UV-vis diffuse reflectance spectra, and porosimetry analysis. The results showed that boron doping could influence the crystal structure, enlarge the BET surface area, improve light absorption ability, and narrow their band-gap energy. The photocatalytic activity of B-doped iron oxides was evaluated in the degradation of atrazine under the visible light irradiation, and B-doped iron oxides showed higher atrazine degradation rate than that of pristine iron oxides. Particularly, B-doped goethite exhibited better photocatalytic activity than B-doped hematite.

1. Introduction

Atrazine, 2-chloro-4-ethylamino-6-isopropylamino-1,3,5-triazine, has been widely used in the fields of corn, sorghum, orchard, and forest, controlling broad-leaf and grassy weeds [1]. However, due to the toxicity to aquatic organisms and mammals, high mobility, low-sorption affinity, and slow biodegradability [2, 3], atrazine has been banned by many European countries. It is frequently detected in ground water and surface water [4] and seriously influenced water quality. Therefore, many ways have been found to resolve atrazine contamination, such as advanced oxidation processes [5], microorganism removal [6], and microwave irradiation [7].

It has been reported that photocatalysis is effective way in the degradation of organic pollutants. TiO2 is considered to be the most promising photocatalyst due to its nontoxicity, chemical inertness, and high reactivity. Parra found that both suspended and supported TiO2 could destroy atrazine although atrazine could not be completely mineralized [8]. However, the widespread technological use of TiO2 is impaired by its wide-band gap (3.2 eV), which can only be activated under UV light. Iron oxides especially goethite and hematite have been studied as photocatalysts in recent years because their lower band gap (2.2 eV), and nonmental doping could improve reactivity of photocatalysts [9, 10]. It is reported that PE films with boron-doped goethite has higher photo-induced degradation than pure PE films under the UV irradiation [11]. In this paper, B-doped goethite and hematite were prepared as photocatalysts, and enhancement of photocatalytic activity of atrazine degradation was observed under visible light irradiation.

2. Experimental

2.1. Materials

Fe(NO3 )3, (CH3 O)3 B, KOH, methanol were supplied from Guoyao Chemical Co. (Shanghai, China) and atrazine was supplied from the Laboratories of Dr. Ehrenstorfer (Germany). All chemicals were used without further purification, and deionized water was used in all the experiments.

2.2. Preparation of Photocatalysts and Characterization

The original goethite (G-S-B0%) was prepared according to the method of Atkinson et al. [12], and the preparation of B-doped goethite photocatalysts was the same as the method of Liao et al. [13], while the atomic weight ratio of B to Fe was 2% (G-S-B2%). Goethite and B-doped goethite were calcined at 400°C for 2 h to obtain the original hematite (H-S-B0%) and B-doped hematite (H-S-B2%), respectively.

The Brunauer-Emmett-Teller surface areas of the powder samples were determined by nitrogen adsorption-desorption isotherm measurements on a ST-08 nitrogen adsorption apparatus. The X-ray powder diffraction pattern was obtained with a Brook D8 diffractometer using Fe K radiation with an accelerating voltage of 40 kV and current of 20 mA. The UV-vis diffuse reflectance spectra of different iron oxides in the 190–900 nm were recorded using an American Lambda35 UV-vis spectrophotometer.

2.3. Photocatalytic Evaluation with Atrazine under Visible Light

The photocatalytic activities of pure and B-doped iron oxides nanoparticles were evaluated by the degradation of atrazine under visible light irradiation at a constant temperature (25°C). 25 mL 10 mg·L−1 atrazine solution was put in 50 mL of centrifugal test tube with 100 mg different photocatalysts, and then all tubes were placed in a constant temperature shaking incubator at a speed of 190 r·min−1. A 250 W metal halide lamp (  nm, JLZ250KN, Shanghai Yaming Co.) was put above all tubes as the visible light irradiation with a distance of 80 cm. At different time intervals during the irradiation, samples were collected, filtered, and finally analyzed by HPLC (Agilent1100). Atrazine was detected at 222 nm and the mobile phase was methanol/water mixture (80 : 20, v/v) at a flow rate of 1.0 mL·min−1 using C18 column (4.6 mm × 150 mm).

3. Results and Discussion

3.1. Crystal Structure

XRD was carried out to investigate the changes of goethite and hematite phase structure after boron doping and heat treatment. Figure 1 shows the X-ray diffraction patterns of goethite and B-doped goethite. Compared with G-S-B0%, there is no significant new peak appearing in G-S-B2%, but the intensity of some peaks become weaker or stronger. Maybe the content of boron is too small to make perceptible crystal change of goethite’s structure by X-ray diffraction. But boron does make an influence in the crystal structure of goethite. Figure 2 shows the crystal form change of common hematite and hematite with 2% boron doping. It seems that H-S-B0% and H-S-B2% have the same peaks. Perhaps the high calcination temperature destroyed the changes of doping.

598713.fig.001
Figure 1: X-ray diffraction patterns of goethite and B-doped goethite.
598713.fig.002
Figure 2: X-ray diffraction patterns of hematite and B-doped hematite.
3.2. UV-vis Diffuse Reflectance Spectra

Figure 3 illustrates the UV-vis light reflection spectrum of goethite and boron-doped goethite. In the UV part, G-S-B0% and G-S-B2% show the same reflection rate, while in the visible part, G-S-B2% shows stronger light absorption than G-S-B0%. The UV-vis light reflection spectra of undoped and 2% boron-doped hematite were shown in Figure 4. H-S-B2% shows stronger absorption than H-S-B0% during the whole wavelength range. The band-gap energy of these four iron oxides were estimated by [14] and presented in Table 1. It is inferred that boron doping may narrow the band-gap energy of iron oxides and improve their light absorption ability.

tab1
Table 1: The properties of different B-doped goethite and hematite.
598713.fig.003
Figure 3: UV-visible light reflection spectrum of goethite and B-doped goethite.
598713.fig.004
Figure 4: UV-visible light reflection spectrum of hematite and B-doped hematite.
3.3. BET Surface Area

Table 1 lists the BET surface areas of four iron oxides. G-S-B2% exhibits higher BET surface area than that of G-S-B0% (34.13%), and the BET surface area of H-S-B2% is also larger than that of H-S-B0%(21.29%). These results confirm that boron doping can efficiently inhibit the crystal size growth and increase the surface area of goethite and hematite.

3.4. Visible Light Photocatalysis of Atrazine

To examine the photocatalytic activity of B-doped iron oxides, atrazine was chosen as target contaminant. And the degradation rate of atrazine through the reaction time in present of these four iron oxides under visible light was displayed in Figures 5 and 6. The photocatalytic degradation of atrazine followed the first-order reaction kinetics under visible light according to , where stands for the initial concentration of atrazine and is the concentration of atrazine at time. All the numbers were collected in Table 2. The results clearly indicated that G-S-B2% and H-S-B2% revealed a substantially enhanced activity for degradation of atrazine, as compared to undoped G-S-B0% and H-S-B0% under visible light irradiation. The first-order kinetics constants for atrazine degradation by G-S-B0%, G-S-B2%, H-S-B0%, and H-S-B2% were 0.0295 h−1 , 0.0301 h−1 ), 0.0199 h−1 , and 0.0202 h−1 , respectively, and the half lives ( ) of atrazine degraded by them were 23.49 h, 23.02 h, 34.82 h, and 34.31 h, respectively. It was confirmed that boron doping could show good optical activity and goethite had better catalytic activity than hematite under visible light irradiation.

tab2
Table 2: Degradation kinetic results of atrazine under visible light irradiation with different iron oxides.
598713.fig.005
Figure 5: Atrazine degradation in present of goethite and B-doped goethite under visible light.
598713.fig.006
Figure 6: Atrazine degradation in present of hematite and B-doped hematite under visible light.

4. Conclusion

The degradation of atrazine by using visible light-activated B-doped iron oxide as photocatalyst is demonstrated in this paper. Goethite, hematite, and B-doped goethite and hematite were successfully synthesized by a novel modified sol-gel method. Although there is no significant different in XRD results between pure iron oxide and B-doped iron oxide, however, the BET surface area and UV-vis spectra indicate that boron doping greatly influenced the properties of iron oxide. G-S-B2% and H-S-B2% exhibited enhanced visible light photocatalytic activity in degradation of atrazine compared with G-S-B0% and H-S-B0%, which maybe due to the stronger light adsorption and boron-doped goethite exhibited better photocatalytic activity than boron-doped hematite.

Acknowledgments

This work was supported jointly by the National Natural Science Foundation of China (40973056; 40371064) and Specialized Research Fund for the Doctoral Program of Higher Education (SRFDP) of the Ministry of Education of PRC (20100146110020).

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