1. Introduction
As one of the fundamental elements of living organisms, nitrogen is essential for both the growth of plants and human production activities such as agricultural and chemical materials production [
1,
2]. The nitrogen element exists mostly in the form of N
2 in air which cannot be directly absorbed by organisms [
3]. In nature, nitrogen can be fixed through microbial action and lightning [
4,
5]. The nitrogen-containing compounds produced by these two methods cannot meet the needs of human life. The Haber-Bosch (H-B) process is the most commonly used industrial nitrogen fixation technology that can supply 40% of the global population with nitrogen demand annually. However, the H-B process heavily relies on fossil energy and causes high CO
2 emissions, exacerbating the greenhouse effect [
6,
7]. Hence, it is necessary to find novel green and sustainable nitrogen fixation technologies.
Plasma is a quasi-electrically neutral system consisting of electrons, charged ions, and neutral particles, which can provide active species to facilitate difficult chemical reactions [
8]. Plasma-based nitrogen fixation can occur in mild conditions, and it has a short startup time and a fast reaction rate. Moreover, the plasma can be driven by clean energy such as solar and wind energy, which is safe and has low pollution and emissions. Hence, it gains an increasing attention among the global scholars. Dielectric barrier discharge (DBD) [
9], microwave discharge [
10,
11,
12], spark discharge [
13], and gliding arc discharge [
14,
15,
16] are widely used to synthesize nitrogen oxides in air, and the gliding arc and microwave plasma have better performance among them. Malik et al. studied the nitrogen fixation by gliding arc, the product gas had no ozone when the air was used as the working gas and it achieved an energy consumption of 15.4 MJ/mol and a NO
x yield of 0.1% [
17]. A millimeter-scale sliding arc reactor operating at atmospheric pressure was proposed by Patil et al. for the synthesis of NO
x [
18]. The energy consumption for NO
x generation was as low as 4.2 MJ/mol, and the NO
x yield was about 1%. Vervloessem et al. proposed a novel atmospheric sliding arc plasma for generating NO
x at different N
2/O
2 gas feed ratios with an energy consumption of 3.6 MJ/mol and a NO
x yield of 1.5% [
16]. Kelly and Bogaerts investigated a microwave plasma using a vortex gas flow to fix nitrogen from the air into NO
x with the lowest energy consumption recorded of 2 MJ/mol at atmospheric pressure, for a total NO
x yield of 3.8% [
12]. Asisov et al. reported the lowest energy consumption of nitrogen fixation, achieved by utilizing a low-pressure electron cyclotron resonance (ECR) microwave discharge in N
2/O
2 mixtures in the early 1980s. Notably, they achieved a NO
x production rate of 14% with an energy consumption of only 0.3 MJ/mol [
19]. However, the results have never been reproduced up to now. Compared to the H-B process which has an energy consumption of 0.5 MJ/mol [
20], it is necessary to study effective means to reduce the energy consumption of the plasma-driven nitrogen fixation.
Catalysts are widely introduced to combine with the plasma to increase NO
x production and decrease the energy consumption of nitrogen fixation [
21,
22]. The synergistic effects of the plasma and catalysts have been shown by previous studies. Patil et al. added the γ-Al
2O
3 to DBD to fix nitrogen in air with an energy consumption of 18 MJ/mol and a NO
x yield of 0.5 %. It was proved that the 5% WO
3/-Al
2O
3 catalyst increased NO
x yield by about 10% [
23]. Xuekai Pei found that the catalyst increased NO
x production even away from the plasma region, which suggested that the catalytic activation of downstream neutrals played an important role [
24]. Mutel et al. reported a yield of 6% NO at an energy consumption of 0.84 MJ/mol in a microwave plasma at 66 mbar with the MoO
3 catalyst [
11]. Metal-organic framework (MOF) catalysts were used in the plasma-driven ammonia synthesis by Shah et al. who used Ni-MOF-74 as a catalyst for ammonia synthesis in synergy with the radio frequency (RF) plasma and it provided a higher ammonia yield of 0.23 g/kWh (on a per gram of catalyst basis) compared to Ni metal [
25]. Most of the existing literature on plasma-driven nitrogen fixation combined with catalysts focused on the use of DBD and RF plasma [
25,
26,
27,
28,
29]. Microwave plasma has the advantages of being electrode-free, having high energy efficiency, and long working life compared with DBD and RF plasmas. The MOF material has advantages over other catalysts, such as a large specific surface area, abundant active sites, and strong adsorption [
30]. Therefore, the MOF material is combined with the atmospheric-pressure microwave plasma for nitrogen fixation in this paper.
Herein, we use CuBTC and ZIF-8 as the MOF catalysts to assist the atmospheric microwave plasma for nitrogen fixation. These two catalysts can effectively improve nitrogen fixation at different flow rates and microwave power, and the catalytic action is better than the general catalyst ZSM-5. And we investigate the TEM images of the catalysts to find out their difference in the particle sizes. The results indicate that CuBTC and ZIF-8, which exhibit higher concentrations of NOx, possess smaller particle sizes compared to ZSM-5.
2. Methods
2.1. Experiment System
Figure 1 shows the photograph of the atmospheric microwave plasma system for nitrogen fixation, which consists of a microwave generator, a circulator (MPWG22CIA01, Mapingtec, Chengdu, China), a water load (MPWG22WLA01, Mapingtec, Chengdu, China), a dual-directional coupler (MPWG22CPA01, Mapingtec, Chengdu, China), a tapered waveguide, a mass flow controller (MFC, KT-C2Z, Ketanyiqi, Zhengzhou, China), and a Fourier transform infrared (FTIR) spectrometer (Vertex 70, Bruker, Wolzbach, Germany). The microwave generator is composed of a water-cooled magnetron (2M265, MUEGGE, Reichelsheim, Germany) and a high-voltage DC power supply (wepex3000BX, Megmeet, Shenzhen, China) that drives the magnetron. The magnetron has a center frequency of 2.45 GHz with a maximum output power of 3 kW. The microwave power meter (KC9532, Measall Technology, Chengdu, China) is internally built into the microwave generator to detect the incident and reflected microwave power. Three ports of the circulator are connected to the microwave generator, the coupler, and the water load, respectively. The coupler is connected to the microwave power meter through two coaxial lines to couple the incident and reflected microwave power for measurement.
A quartz tube with an inner diameter of 25 mm, an outer diameter of 29 mm, and a length of 30 cm is inserted into the tapered waveguide to restrict the plasma. A condenser tube surrounds the quartz tube for cooling. When the plasma is excited, the gas passes through the catalyst and then is detected by the FTIR spectrometer above the quartz tube.
The gas flow rate is adjusted by the MFC which has a range from 1 L/min to 22 L/min. Air is taken as the working gas and it flows into the quartz tube in the form of a swirl to reduce the heat load of the quartz tube. The concentration of NOx is obtained by measuring the infrared absorption spectrum of the output gas using the FTIR spectrometer locating after the catalyst position. The catalyst is placed in the downstream area which is away from the plasma torch. This area consists of reactive oxygen and nitrogen species (RONS), and NO will react sufficiently with O2 to produce NO2, which can be seen in our measurement results in section 2.4.
2.2. Catalyst Characterization
In this paper, three catalysts including CuBTC, ZIF-8, and ZSM-5 are used to assist the atmospheric microwave plasma for nitrogen fixation. Both CuBTC and ZIF-8 are MOF materials made by mechanochemical and aqueous methods, respectively. ZSM-5 is the zeolite catalyst. All the catalysts are made by XFNANO Company (Jiangsu, China). MOF catalysts are preheated before each experiment. The weight of catalysts used in each experiment remains at 200 mg.
Figure 2 shows the pictures of three catalysts prior to usage.
CuBTC is in a light blue powder form composed of Cu and benzene-1,3,5-tricarboxylate with a pore size of 0.9 nm, and a specific surface area of about 457 m2/g. It needs to be heated at 600 ℃ for three hours before use. ZIF-8 is composed of Zn2+ and C4H5N2- with a pore size of 0.34~1.16 nm and a specific surface area of about 1,345 m2/g, which needs to be preheated at 1000 ℃ for ten hours. ZSM-5 is a kind of white powder with a silicon to aluminum ratio (SiO2/Al2O3) of 25-30 wt %. The specific surface area is 340 m2/g and the pore size is about 5 nm.
2.3. Catalyst Location Determination
In this work, the working temperature of both CuBTC and ZIF-8 should be below 1000 ℃ to avoid inactivation [
31,
32]. However, the gas temperature of the microwave plasma is usually higher than 1000 ℃, making it difficult to directly measure this high temperature [
33]. Therefore, the temperature distribution of the plasma is simulated to determine a suitable location for placing the catalyst. Moreover, the simulation result is verified by measuring the temperature points below 1000 ℃ using a digital thermometer. For this measurement, the sensor of the thermometer was placed directly in the specific location of plasma to obtain the temperature value.
Figure 3 shows the temperature simulation model consisting of a condenser tube, a quartz tube, a condensing device, and a waveguide. Both the condenser tube and condensing device are used to cool the quartz tube when the plasma is generated.
The working gas flows into the quartz tube from its bottom which is 2.2 cm away from the center of the waveguide. In the simulation, we ignore the swirling form of the inlet gas in front of the quartz tube, and the gas flow in the quartz tube is assumed to be a laminar model. Then the fluid velocity can be solved by the Navier-Stokes equation [
34].
where
is the fluid density with a unit of kg/m
3,
is the velocity vector of the fluid with a unit of m/s,
denotes the net flow of momentum out of a unit volume space,
indicates the stress tensor,
is the pressure with a unit of Pa,
is the viscous stress, and
is the external force per unit volume of fluid. The plane F is set as the air inlet and plane A is the gas outlet. For the water flow, the planes B and C are set as the inlet and outlet of the condenser tube, while the planes D and E are assigned to be the inlet and outlet of the condensing device. The boundaries of the condenser tube, quartz tube, condensing device, and waveguide are all set as the wall boundaries which have zero velocities.
The gas temperature T is solved by the heat transfer function [
35].
where
is heat capacity with a unit of J/(kg·K),
k is the thermal conductivity,
is the temperature gradient, and
Q is the heat source. The initial temperature at the plasma core located at the waveguide center is set to be 5300 ℃, which is a measured temperature of the atmospheric microwave air plasma [
36]. The planes B, D, and F are all set as the inflow boundaries with an initial temperature of 19 ℃. The corresponding outflow boundaries are the planes C, E, and A, respectively. The outer boundaries of the condenser tube, quartz tube, condensing device, and waveguide are all set as the convection heat flux
q, which is expressed as [
37].
where
h is the heat transfer coefficient of air with
h = 10 W/(m
2·K), and
Text is the temperature of air assumed to be 19 ℃. The initial temperature of the simulation domain is also set as 19 ℃.
The commercial software COMSOL Multiphysics was adopted for the calculation in this paper. The free tetrahedral meshes with the maximum and minimum sizes of 13 mm and 0.13 mm, respectively, are generated for the simulation domain. The total mesh number is 873403 with 86641 unknowns. All the computations are calculated by a workstation with the configuration of Intel(R) Xeon(R) E5-2650 CPU at 2.3 GHz and RAM 96 GB based on the 64-bit Windows10 platform.
The x-z cross-section view of the simulated temperature distribution is shown in
Figure 4. It is clear that the gas temperature in the quartz tube decreases gradually with the direction of airflow. The condensing equipment has a significant effect on cooling the quartz tube as the temperature inside the quartz tube in the waveguide is significantly higher than that in other areas of the waveguide. It can be seen from
Figure 4 (b) that the temperature distribution in the x-y cross section of the quartz tube exhibits a divergent pattern with high central temperature and low edge temperature.
Figure 5 shows the specific temperature values of the points on the z-axis. As z increases, the temperature will decrease. According to
Figure 5, the gas temperature will be below 1000 ℃ when z is greater than 18 cm. Therefore, we measured the temperature values at z = 19.7, 20, 29, 40.5, and 50 cm shown as the red points in
Figure 5. The measured temperatures are in good agreement with the simulation results. As the catalysts used in this paper can work at 600 ℃ [
31,
32], the location of z = 24 cm with a maximum temperature of 600 ℃ is selected as the catalyst position.
2.4. NOx Measurement
The infrared absorption spectra of the gases generated by microwave plasma in different conditions are detected to determine the NO
x concentrations.
Figure 6 shows the spectrum at the gas flow rates of 9 L/min and the microwave power of 450 W. It can be observed that the NO
x mainly consists of NO
2 and NO [
38]. Moreover, the concentration of NO
2 is much higher than that of NO since most of the NO will react with the oxidative species to produce NO
2 at the measurement area. Thus, the total concentrations of NO
2 and NO are determined as the NO
x concentrations in this paper.
Figure 7(a) and (c) show the infrared absorption spectra of NO and NO
2 with standard concentrations measured by FTIR. According to the absorption peaks at 1905 cm
-1 for NO and 1627.8 cm
-1 for NO
2 [
38], the calibration curves for NO and NO
2 are built as shown in
Figure 7(b) and (d) to determine their concentrations. The relationship between the concentration and absorbance of these two curves is approximately linear.
The energy consumption is calculated by the following formula,
where
is the energy consumption with a unit of MJ/mol, P represents the microwave power,
Lm is the molar volume of ideal gas at atmospheric pressure and room temperature which equals to 24.05 L/mol,
is the NO
x concentration with a unit of ppm (parts per million), and
fl is the gas flow rate with a unit of L/min.
3. Experiment Results and Discussions
In the experiment, three different catalysts are placed in the same position determined in section 2.3, and the nickel foam is fixed there as the catalyst carrier due to its cheapness and high temperature resistance. The blank group indicates no nickel foam and catalyst packed downstream of the microwave plasma, and the nickel foam group which has no catalyst is taken as the control group. The NOx concentration and energy consumption are obtained at different microwave power and gas flow rates.
3.1. NOx Production
Figure 8 shows the NO
x concentrations with gas flow rates ranging from 3 L/min to 13 L/min at four different microwave power. The NO
x concentration in the blank group is similar to that in the control group, which indicates that the nickel foam has little effects on the production of NO
x. The NO
x concentrations are higher in the three catalysts than in the control group, showcasing that three catalysts can promote the synthesis of NO
x. Among these catalysts, CuBTC and ZIF-8 have higher NO
x concentrations than ZSM-5.
As the microwave power remains constant, the NO
x concentration firstly increases and then decreases with the increment of gas flow rate. This is consistent with the trend of the visible length of the plasma changing with the gas flow rate [
36]. When the gas flow rate is 3 L/min, the plasma torch is short leading to a small reaction area. As the gas flow rate slowly increases from 3 L/min to a medium flow rate range of 7 L/min to 9 L/min, the length of the plasma torch increases, which results in a bigger reaction area for NO
x synthesis. When the gas flow rate is too high, the propagation distance of the surface wave that maintains the plasma becomes short, causing a decrement of the plasma torch length [
39]. Moreover, the gas residence time is also getting smaller at high gas flow rates, hence, the NO
x concentration is rapidly reduced. When the microwave power increases from 450 W to 700 W, the gas flow rate corresponding to the maximum NO
x concentration increases from 5 L/min to 9 L/min. When the gas flow rate remains constant, the NO
x concentration increases as the microwave power increases due to the increment of the specific energy input (SEI) which is written in Equation (5) [
23]. As the energy gained per unit volume of gas increases, more N
2 and O
2 will participate in the reaction, thus increasing the NO
x concentration.
When the microwave power is 700 W and the flow rate is 9 L/min with CuBTC, the maximum NOx concentration of 33400 ppm in the experiment is obtained. Comparing the results of CuBTC and blank group, the NOx concentration can be increased from 28000 ppm to 32800 ppm with a maximum increment of 17.1% under the condition of 9 L/min and 550 W.
3.2. Energy Consumption
Figure 9 shows the energy consumption of the nitrogen fixation under the same conditions with
Figure 8. It is found that three catalysts can decrease the energy consumption of nitrogen fixation. As the gas flow rate increases while the microwave power keeps constant, the energy consumption will decrease. According to Equation (4), the energy consumption is inversely proportional to the NO
x concentration and gas flow rate, and directly proportional to the microwave power. When the microwave power remains constant and the gas flow rate increases from 3 to 5 L/min, the energy consumption decreases rapidly because the NO
x concentration increases as the gas flow rate. When the gas flow rate increases gradually from 5 L/min to a medium flow rate (7 to 9 L/min), the energy consumption reduces slowly due to the slow increment or even decrement of NO
x concentration. When the microwave power is at high levels such as 650 W and 700 W, and the gas also flows at high rates of 11 and 13 L/min, the energy consumption almost levels off due to the very rapid decrement in NO
x concentration.
At different microwave power and gas flow rates, the energy consumption with ZSM-5 is higher than that with CuBTC and ZIF-8. The minimum energy consumption obtained in the experiment is 2.05 MJ/mol, which is reduced by 10.1% compared to no catalyst. It is achieved by using CuBTC as the catalyst at the microwave power of 550 W and the gas flow rate of 13 L/min. Compared to the results of the blank group, the energy consumption in the experiment is reduced maximally by 14.6% using CuBTC at 9 L/min and 550 W.
3.3. Particle Size of the Catalysts
In order to find out the particle size of the catalysts before and after usage, this paper employs a transmission electron microscope (HT7800, Hitachi, Tokyo, Japan) to capture TEM images of the catalysts, as depicted in
Figure 10. When compared to
Figure 2, it is evident that CuBTC has undergone a transformation into the black color, indicating that Cu has been oxidized to CuO. Before usage, CuBTC exhibits the smallest particle size of approximately 408 nm, whereas ZIF-8 has a moderate particle size of about 503 nm, falling between CuBTC and ZSM-5, as illustrated in
Figure 10(
b). Comparing these results with
Figure 8, it suggests that the NO
x concentration produced in CuBTC and ZIF-8, which have smaller particle sizes, is greater than that in ZSM-5 with a larger particle size. This conclusion agrees well with the findings of Patil et al., as catalysts with smaller particle sizes generate a high-intensity localized electric field and result in a higher intensity of micro-discharges [
23,
40]. After the experiments, the particle sizes of CuBTC, ZIF-8, and ZSM-5 all increase, following the order: CuBTC > ZIF-8 > ZSM-5, as shown in
Figure 10(
c).
4. Conclusions
In this paper, the effect of MOF materials on nitrogen fixation by microwave plasma at atmospheric pressure is investigated. The experimental results show that the MOF materials of CuBTC and ZIF-8 can effectively increase NOx production and reduce energy consumption at different microwave power and gas flow rates, and the improvement effect surpasses that of the general catalyst ZSM-5. The maximum NOx concentration obtained in the experiment reaches 33,400 ppm and the minimum energy consumption is 2.05 MJ/mol. Compared to the results without the catalyst, the energy consumption is reduced by 14.6% and the NOx production is increased by 17.1%. The TEM results of the catalysts reveal that MOF materials, which exhibit higher concentrations of NOx, have smaller particle sizes in comparison to the general catalyst ZSM-5 prior to usage. Furthermore, all the catalyst particle sizes get enlarged after the nitrogen fixation experiments. This paper verifies the superiority of combining atmospheric microwave plasma with MOF catalysts for nitrogen fixation, benefiting to the industrial promotion of plasma-based nitrogen fixation technology.
Author Contributions
Conceptualization, W.X.; methodology, F.Z.; software, F.Z.; validation, S.W.; formal analysis, K.F. and S.W.; investigation, K.F.; resources, F.Z.; data curation, K.F. and S.W.; writing—original draft preparation, F.Z.; writing—review and editing, W.X.; visualization, F.Z.; supervision, W.X.; project administration, W.X.; funding acquisition, W.X. All authors have read and agreed to the published version of the manuscript.
Funding
This research was funded by the National Natural Science Foundation of China under grant number 62101146 and the Guizhou University Talent Project under grant number 2020-51.
Data Availability Statement
The original contributions presented in the study are included in the article, further inquiries can be directed to the corresponding author.
Conflicts of Interest
The authors declare no conflicts of interest.
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