Removal of methyl orange from water by Fenton oxidation of magnetic coconut-clothed biochar

Water pollution has become a serious environmental problem to date. Advanced oxidation processes (AOP) have been widely applied in water treatments. However, the traditional Fenton reaction based on the Fe2+–H2O2 system has obvious drawbacks, limiting further practical applications. In this work, an Fe3O4 and nano-clothed biochar (Fe3O4/CBc) composite was prepared through a precipitation method and used for the degradation of methyl orange (MO) in water. The Fe3O4/CBc composite was characterized by FTIR, BET, SEM, TEM, XRD, and VSM. In addition, the adsorption/catalytic oxidation of MO were also tested. Specifically, Fe3O4/CBc had a rough surface, abundant porous structure, high surface area of 835.82 m2 g−1, and obvious magnetization. The catalyst showed rather high performance towards MO removal. The optimal conditions for MO removal were as follows: the dosage of hydrogen peroxide was 16 mmol L−1, pH = 3, the temperature was 35 °C, and the addition amount of adsorbent was 10 mg. Under optimal conditions, the MO removal rate can be higher than 99%. The synergistic effect between catalytic degradation and adsorption in removing MO was also observed. Besides high performance in removing MO, Fe3O4/CBc also exhibited high stability, easy magnetic separation, and great reusability, as well as the potential to be developed as a new heterogeneous Fenton catalyst.


Introduction
With the continuous development of modern industry, water pollution is becoming more and more serious. For example, the textile industry is one of the most important industries. There are many production processes in this industry, which have produced highly polluted wastewater containing dyes with different structures. If the treatment method is improper, this kind of wastewater has color and toxicity, which will cause serious environmental problems. Therefore, it is urgent to develop efficient approaches to control water pollution. As compared with other advanced oxidation processes, the Fenton reaction 1 is an advanced oxidation method with the advantages of mild conditions, low cost, and high efficiency. It can oxidize and degrade almost all kinds of organic pollutants without selectivity. 2,3 Therefore, it has been widely used in wastewater treatments in areas like papermaking, printing, dyeing, etc. Unfortunately, the traditional Fenton reaction 4-6 usually suffers from several defects including difficult reuse of catalyst, low utilization of H 2 O 2, and easy production of iron sludge. Thus, it would be of great importance to improve the Fenton system 7 in water treatment.
Fe 3 O 4 NPs have the characteristics of super-paramagnetism, great thermal stability, high reaction activity, and simple preparation. [8][9][10] They can replace Fe 2+ in the traditional homogeneous Fenton reaction and stimulate H 2 O 2 to produce cOH as a new Fenton reaction catalyst. It not only retains the characteristics of high catalytic activity of Fenton reaction, but also utilizes magnetic separation with efficient recovery, which might overcome the defects of homogeneous Fenton reactions and attract extensive attention. In this work, a superparamagnetic Fenton catalyst (Fe 3 O 4 /CBc) was fabricated by loading Fe 3 O 4 NPs on coconut-clothed biochar 11,12 through an in situ precipitation procedure. 13 Methyl orange (MO) was selected as the target pollutant to evaluate the degradation performance of organic contaminants. The effects of addition amount, H 2 O 2 content, pH, temperature, and free radical inhibitor on MO removal were also studied. 14 water (50 mL) were placed in a 100 mL glass beaker. The mixture was stirred for 2 h, which was then placed into an oven at 80 C for drying. The dried sample was placed in a quartz boat and pyrolyzed at 700 C for 270 min with a heating rate of 10 C min À1 under the protection of pure nitrogen. Aer cooling down naturally, the sample obtained was washed to neutral and dried at 70 C under the vacuum.
Preparation for Fe 3 O 4 /CBc. Deionized water (300 mL) was added into a 500 mL three-port ask equipped with a mechanical stirring device. Nitrogen was purged into the ask for 30 min to remove the air inside the ask. Then FeCl 3 $6H 2 O (4.49 g, 16.61 mmol) and FeSO 4 $7H 2 O (2.31 g, 8.30 mmol) were added and stirred for 20 min to obtain a homogeneous orangered solution. Then CBc (1.9 g, the mass ratio of CBc and Fe 3 O 4 is 1 : 1) was added and stirred for another 3 h before adjusting the pH to about 10 using NH 3 $H 2 O. The obtained black suspension was aged at 60 C for 4 h, followed by cooling down naturally, separating by a magnet, washing with deionized water ve times and C 2 H 5 OH three times, and drying at 60 C under the vacuum over 20 h. Finally, the biomass carbon composite was obtained and named as Fe 3 O 4 /CBc. Samples with other proportions (m(CBc) : m(Fe 3 O 4 ) ¼ 3 : 1, 2 : 1) were also prepared through the same above experimental steps.

MO Removal experiments
Methyl orange solution (25 mL, 100 mg L À1 ) was added into a 50 mL conical ask to simulate wastewater. The pH of the solution was adjusted with 0.1 mol L À1 hydrochloric acid or sodium hydroxide. Aer adding a certain mass of H 2 O 2 and Fe 3 O 4 /CBc, the mixture was vibrated for 120 min under room temperature. Aer that, the concentration of methyl orange was measured using visible spectrophotometry.

Characterizations
Brunauer-Emmett-Teller (ASAP2460) was used to measure the nitrogen adsorption capacity of samples at 77 K and the specic surface area of each sample. Scanning electron microscopy (JSM-7401F) and Transmission electron microscopy (JEM-F200) were employed to record the micro surface morphology of materials. Fourier transform infrared spectroscopy (FT-IR6700) was used for further infrared spectrum analysis of materials. Xray diffraction (UItima IV) was utilized to test the crystal structure of materials. Vibrating sample magnetometer (SQUID-VSM) was used to test the hysteresis loop of catalyst. The concentration change of methyl orange solution was analyzed by a ultraviolet-visible spectrophotometer (UV, 752N).

SEM, TEM, and EDS analysis
The morphology and structure of the as-prepared catalysts were characterized by SEM and TEM. As shown in Fig. 1a and d, the CBc had a rather rough surface with numerous porous structures, 15,16 and the Fe 3 O 4 nanoparticles had an average diameter of about 50 nm and the surface was rough, which can be attributed to the fact that each Fe 3 O 4 nanospheres are composed of many smaller particles. The EDS spectrum in Fig. 1c showed that the composite contains C, O, and Fe. As seen in Fig. 1d, the particle size of Fe 3 O 4 was about 50 nm. From the HRTEM image ( Fig. 1e) of the Fe 3 O 4 /CBc 17 diagram of the composite, the lattice stripes were 0.292 and 0.249 nm, respectively, which were corresponding to the 220 and 311 facets of Fe 3 O 4 respectively, conrming that these NPs were Fe 3 O 4 .

BET analysis
The surface area and the porosity of the CBc and Fe 3 O 4 /CBc were summarized in Fig. 2. In Fig. 2, the surface area of the CBc was higher as compared to the surface area of the Fe 3 O 4 /CBc. The immobilization of the Fe 3 O 4 on the biochar surface didn't provide the additional surface area for adsorption, which is possible due to the particles clogged the pores in the surface of the biochar. In fact, the pore volume of the Fe 3 O 4 /CBc was slightly lower as compared to that of the CBc, which changed from 0.475 cm 3 g À1 to 0.411 cm 3 g À1 . It indicated that the introduction of Fe 3 O 4 nanoparticles can make the surface of the material rough, in which the nanoparticles were overlapped and piled up with each other, resulting in the reduction of the empty volume and the decrease of the specic surface area.

FT-IR analysis
The IR spectra of the CBc and Fe 3 O 4 /CBc were shown in Fig. 3. CBc and Fe 3 O 4 /CBc composite had roughly the same absorption peaks. The adsorption peaks around 3420, 891, and 1620 cm À1 can be assigned to the stretching vibration peaks of O-H, C]C, and C]O, respectively, indicating that the surface of the composite was rich in oxygen-containing functional groups, which was conducive to the adsorption of organic compounds. Specically, Fe 3 O 4 /CBc showed an absorption peak at 607 cm À1 in the infrared image, which was the bending vibration peak of Fe-O-Fe, 18,19 suggesting that Fe 3 O 4 was successfully loaded on the surface of coconut-clothed biochar.

XRD analysis
As shown in Fig. 4 There was no hysteresis phenomenon. Furthermore, the values of residual coercivity and magnetization were zero, which reects that the target materials were superparamagnetic. 20 Although the saturation magnetization of the composite was less than that of Fe 3 O 4 , the value was still higher than 16.3 emu g À1 , 21 which was required for general magnetic separations. Therefore, Fe 3 O 4 / CBc can be easily separated through the external magnetic eld, which can be further conrmed by the rapid magnetic separation of the catalyst.

Removal effect of MO under different conditions
As shown in Fig. 6, the removal effect of MO was studied under different conditions. The initial temperature was 25 C, the initial pH was 3.0, the amount of catalyst was 5 mg and the concentration of 30% H 2 O 2 was 16 mmol L À1 . The

Effect of the amount of Fe 3 O 4 /CBc and H 2 O 2 on the degradation of MO
The effect of Fe 3 O 4 /CBc and H 2 O 2 usages on the MO removal were shown in Fig. 7 and 8, respectively. The MO removal rate increased from 41.9% to 99.4% as Fe 3 O 4 /CBc usage raised from 1 mg to 10 mg. In addition, the removal rate of MO was enhanced with the increase of Fe 3 O 4 /CBc amount. When the addition amount of catalyst was xed to be 5.0 mg, the MO removal rate increased from 70.2% to 76.8% as the hydrogen peroxide usage increased from 10 to 100 mL. When the addition amount of hydrogen peroxide exceeds 16 mmol L À1 , the removal rate of MO also decreased slightly.
According to research reports, we proposed the possible mechanism of the Fenton reaction as follows:

Effect of initial pH value on MO degradation process
At an ambient temperature of 25 C, the dosage of Fe 3 O 4 /CBc was 5 mg and the concentration of 30% hydrogen peroxide was 15.99 mmol L À1 . The inuence of the solution pH values on the MO degradation was also studied, as is shown in Fig. 8. As seen from Fig. 9a that the pH of the solution has a great inuence. With the pH value between 5 and 8, the removal efficiency was low, which should be attributed to the formation of hydrate iron and hydrated ferrous complexes. Since the divalent iron ions cannot be effectively dissociated, the generation of cOH was inhibited, resulting in the obvious weakening of the oxidative degradation ability of Fenton system. 24 In this case, the removal of MO mainly depended on the adsorption of catalyst materials. When the pH of the solution was between 2 and 4, there was electrostatic adsorption between Fe 3 O 4 /CBc and MO, which increases the adsorption capacity of MO at lower pH, as well as the contact of active sites, and eventually improves the degradation rate. When the pH value was 4, the MO removal rate was 53.3%, and when the pH value was 3, the MO removal rate reached up to 78.6%. So the best removal rate can be obtained with the pH at 3.
In Fig. 9b, when the pH values were 4, 3 and 2, the dissolution amount of Fe were 0.34 mg L À1 , 3.89 mg L À1 and    12.6 mg L À1 respectively. The dissolution amount of Fe increased as the pH decreases. The change of Fe dissolution amount can directly reect the relationship between MO removal rate and pH value. Finally, Fe 2+ produced in Fenton system reached up to the critical value when the pH value was 3; 25 When the pH value was 2, because the dissolution of Fe exceeded the adjacent value, the free radical quenching reaction between H 2 O 2 and cOH occurred, resulting in the decrease of the concentration of hydrogen peroxide and cOH in the system. At the same time, due to the synergistic effect of adsorption, the MO removal rate did not signicantly change. Considering the environmental impact and the analysis of the experimental results, the optimal pH value in the experiment was 3.

Effect of ambient temperature on the degradation process of MO
When the initial pH of the solution was 3, the dosage of Fe 3 O 4 / CBc was 2 mg and the dosage of H 2 O 2 was 16 mmol L À1 . The effect of temperature on the MO removal process was shown in Fig. 10. The experimental results showed that at 25 C, 35 C, and 45 C, the removal rates of MO were 78.9%, 82.2%, and 87.3% respectively. It was proved that a higher temperature can facilitate the removal of MO due to the higher dissolution of Fe and the faster reaction rates at a higher temperature. However, if the temperature was too high, the decomposition rate of hydrogen peroxide was also accelerated and additional facilities or equipment were required to maintain the reaction temperature, resulting in a large amount of energy consumption. Therefore, based on the cost assessment, the reaction was carried out at room temperature. Since the heat energy can be improved in combination with the production process, 35 C would be the best treatment temperature.

Effect of inhibitors on MO degradation
MO degradation reaction was carried out by the Fenton reaction, 26,27 which depends on the strong oxidizing free radical cOH produced by the system. Therefore, the free radical scavenger in the reaction system would have a very direct impact on the degradation process of MO. In the experiment, the dosage of When the initial pH of the solution was 3 and the temperature was 25 C, t-butanol was used as a free radical scavenger to explore the relationship between the removal effect of MO and the addition amount of t-butanol. The experimental results were shown in Fig. 11. There was a close relationship between the MO removal rates and the additional amounts of tert butyl. With only 10 mL t-butanol addition, the MO removal rate decreased drastically from 99.6% to 86.3%. When the t-butanol usage reached up to 39 mmol L À1 , the MO 28 removal rate decreased to only 60.5%. When the addition amount of tbutanol continued to increase up to 78 mmol L À1 , the MO removal rate was no longer changed. According to the experimental data, when the amount of t-butanol was more than 39 mmol L À1 , the Fenton system was almost completely inhibited, resulting in the complete stop of oxidative degradation, the MO removal mainly depended on the adsorption of MO by Fe 3 O 4 /CBc (Fig. 7, the adsorption of MO on Fe 3 O 4 /CBc was 59.5% without H 2 O 2 ). Therefore, the existence of free radical inhibitors like t-butanol should be avoided in the Fenton reaction system.

Catalyst regeneration performance
When the initial pH of the solution was 3, the ambient temperature was 25 C, the dosage of Fe 3 O 4 /CBc was 10 mg and the dosage of H 2 O 2 was 16 mmol L À1 to test the reuse efficiency of the catalyst. Aer the experiment, the Fe 3 O 4 /CBc was separated by magnetic separation, washed with deionized water and microwaved for 1 h, and reuse 4 times. The experimental data were shown in Fig. 12. Aer the catalyst was utilized ve times, the MO removal rates showed a downward trend, and the removal rates of MO were 99.4%, 98.2%, 94.3%, and 86.7% respectively. Although the removal efficiency slightly decreased, it was still higher than 85%, indicating that it had a great reuse rate. There might be two reasons for the decline of the MO removal effect. On the one hand, there was a certain loss of Fe 3 O 4 in the degradation process. The dissolution amount of Fe decreased from 3.89 to 2.67 mg L À1 with the increase in catalyst use times, resulting in the decline of catalytic efficiency. On the other hand, some MO molecules were rmly adsorbed on the material surface, which occupied the adsorbed active sites and cannot be effectively removed by activation. In a comprehensive analysis, Fe 3 O 4 /CBc was stable, 29,30 easily separately, and had a high reuse efficiency.

Conclusion
In summary, a Fe 3 O 4 and coconut-clothed biochar (Fe 3 O 4 /CBc) composite is prepared through a precipitation method and employed for the degradation of methyl orange (MO) in water. The Fe 3 O 4 /CBc composite was characterized by FTIR, BET, SEM, TEM, XRD, and VSM. The adsorption and catalytic oxidation of MO were also tested. Specically, Fe 3 O 4 /CBc has a rough surface, abundant porous structures, a high surface area of 638.10 m 2 g À1 , and obvious magnetization. The catalyst showed rather high performance towards MO removal. The optimal conditions for MO removal were obtained as follows: the dosage of hydrogen peroxide was 16 mmol L À1 , pH ¼ 3, the temperature was 35 C, and the addition amount of adsorbent was 10 mg. Under optimal conditions, the MO removal rate can be higher than 99.4%. The synergistic effect between catalytic degradation and adsorption in removing MO was also discovered. Besides high performance in the depredating MO, Fe 3 O 4 / CBc also exhibited high stability, easy magnetic separation, and good reusability, as well as the potential to be developed as a new heterogeneous Fenton catalyst.

Conflicts of interest
There are no conicts to declare.