1. Introduction
Human activities lead to the emission and generation of greenhouse gases. The removal of already-emitted greenhouse gases can be achieved through methods such as forest absorption or carbon capture utilization and storage (CCUS). The goal is to reduce current greenhouse gas emissions to zero. Carbon neutrality became a hot topic in the international community in 2018 when the United Nations Intergovernmental Panel on Climate Change (IPCC) stated in its “Global Warming 1.5 °C special report” that the global temperature should not rise more than 1.5 °C [
1].
A lot of effort is being made to achieve carbon neutrality around the world, and Korea has also recently been sequentially pursuing related policies to achieve carbon neutrality. Hydrogen is attracting attention as a technology that can achieve carbon neutrality because it is environmentally friendly.
Hydrogen has the advantage of being a clean fuel that can be used as an energy storage medium. So far, global hydrogen production has been carried out using the cost-competitive steam methane-reforming (SMR) method, but this has been accompanied by high emissions of carbon dioxide and consumption of fossil resources. Eco-friendly hydrogen production technology through water electrolysis using electricity obtained from renewable energy is an attractive technology but is not widely available due to low price competitiveness.
As a measure of greenhouse gases, gray, green, blue, and turquoise color codes have been assigned to hydrogen production technology by the IEA, and there is a lot of interest in green hydrogen and turquoise hydrogen as clean hydrogen [
2,
3].
Byproduct hydrogen and reformed hydrogen are classified as gray hydrogen. Be-cause byproduct hydrogen is generated incidentally in petrochemical and steel manufacturing processes, there are limits to increasing production. Reformed hydrogen using natural gas has the advantage of being able to be mass-produced, but it has been pointed out that a large amount of carbon dioxide is produced as a byproduct.
Blue hydrogen is what complements the limitations of gray hydrogen. The production method is the same as that of gray hydrogen, but it is called clean hydrogen because the carbon dioxide generated during the production process is removed using CCUS technology. The captured carbon dioxide is permanently stored or used in cement, semiconductor gas, tire materials, etc. Blue hydrogen has been evaluated as the most realistic alternative for expanding the hydrogen industry.
Green hydrogen is a technology that produces electricity by decomposing water using electricity generated from renewable energy such as solar power or wind power and is attracting attention as the ultimate clean energy because it does not emit carbon dioxide. However, economic and technical limitations must be overcome in order to mass produce green hydrogen, such as using water electrolysis production facilities and renewable energy. In addition, hydrogen produced by decomposing water using the existing power grid rather than renewable energy is called yellow hydrogen, and hydrogen produced by decomposing water using electricity generated through nuclear power generation is called pink hydrogen [
4].
Additionally, hydrogen produced by methane pyrolysis is called turquoise hydrogen, and it is potentially one of the most promising technologies in the field of clean hydrogen production. The biggest advantage of this technology is that can decompose methane into hydrogen and solid carbon without using traditional oxidizers. In this case, no carbon oxides are emitted, and the solid carbon can be removed from the reactor and later used as a commercial byproduct. This also eliminates the need for expensive CCS facilities. It is a promising feedstock for hydrogen production, especially since the infrastructure for the production, storage, and transportation of natural gas is sufficiently well developed worldwide.
The direct decomposition of methane into hydrogen and carbon is an endothermic process with a single-stage reaction [
5,
6,
7].
Technological variants of methane pyrolysis are divided into three categories, depending on the predominant method of energy exposure and reaction conditions: thermal decomposition, plasma decomposition, and catalytic decomposition [
8].
Among these, one method for methane pyrolysis is to use plasma, and the pyrolysis energy demand is supplied by electricity. Methane decomposes into hydrogen and carbon byproducts through thermal decomposition via plasma discharge. Unlike other pyrolysis process technologies, plasma has a fast start-up, allowing for flexible reactor operation. Hydrogen production can therefore be easily scaled to match the availability of renewable electricity [
9,
10,
11,
12].
Monolith, a company that commercializes the methane pyrolysis process using a plasma heat source, has been operating since 2012. In 2020, it produced 14,000 tons of black and 2500 tons of hydrogen. Monolith’s plasma source relies on technology for the simultaneous production of hydrogen and carbon black based on plasma (2000 °C) using 100% renewable energy in the form of arc discharge [
13]
When decomposing hydrocarbons using plasma, a lot of electricity is consumed and the durability of the burner that generates the plasma is short due to the instantaneous high temperature. During plasma discharge, disadvantages of unstable discharge and low conversion of methane arise due to the interference of the methane reaction due to carbon growth as a plasma electrode. Therefore, it is important to design a plasma reactor to overcome these problems.
In this study, we designed and manufactured an arc plasma reactor and confirmed the possibility of a scaled-up design via gas analysis along with the phenomenon of hydrogen and carbon black generation through arc discharge after supplying methane.
2. Materials and Methods
2.1. Plasma Torch and Chamber Reactor
To study the characteristics of methane thermal cracking using plasma, a plasma torch and chamber reactor were manufactured, as shown in
Figure 1.
The plasma supply system consists of a plasma torch, a plasma power supply, a plasma transfer gas supply, and a cooling water supply facility. For the plasma supply device, a non-transferred arc plasma torch was selected and manufactured at the 10 kW level for methane cracking at a feed rate of 1 to 10 L/min. Nitrogen gas was used as the plasma transfer gas to discharge the arc of the non-transferred plasma torch. In addition, a coolant circulation system was applied to cool the plasma electrode and the main body, and the thermal efficiency of the plasma torch could be evaluated by measuring changes in the coolant circulation flow rate and temperature.
The plasma chamber reactor was manufactured using stainless steel (STS-304) with a diameter of 60 mm to fit the plasma torch and a height of 480 mm based on the plasma flame length. The plasma torch was mounted at the top center of the reactor and the plasma flame was formed from top to bottom. To maintain parallel flows of plasma and reaction gas, the fuel inlet and product gas outlet were installed at the upper and lower sides of the reactor, respectively, to supply methane and discharge generated gas.
Methane was supplied in two ways, and the reaction characteristics based on the supply method were compared and evaluated. One way was to supply methane through a gas inlet installed on the upper side wall of the reactor (type A), and the other was to supply methane through a hybrid burner (Type B) located between the torch and the reactor, as shown in
Figure 2.
Hybrid burners supplied methane close to the plasma flame by extending the methane supply line toward the center of the reactor. Additionally, cooling water was supplied to prevent damage to the methane supply lines due to a high-temperature plasma flame.
Thermocouples and pressure transmitters were installed to measure temperature and pressure changes inside the reactor and monitor the reaction status. In consideration of material deformation, a clamp-fastening method was applied to fix the cylindrical refractory in front of the gas outlet. After the plasma discharge was completed, the inside of the reactor was inspected to check for any abnormalities.
2.2. Instrumentation and Setup
The system for the arc plasma reaction experiment consisted of a gas supply section, a plasma reaction section, a cooling water circulation section, and a generated gas analysis section, as shown in
Figure 3.
In the gas supply section, nitrogen gas (99% purity) for arc plasma discharge and methane (99.99% purity) for the reaction were supplied in fixed quantities via a mass flow controller (MFC, Brooks). First, the nitrogen supply was started, and then the plasma discharge was started while maintaining the nitrogen flow. When a stable plasma discharge state was confirmed, the reaction began by supplying methane.
The gaseous products from the methane plasma reactions were cooled and then discharged through a carbon capture filter (Teflon cartridge filter), and solid carbon particles generated during the reaction were captured by the filter (
Figure 3c). The amount of solid carbon production was calculated by measuring the change in weight of the filter before and after the reaction. All weights of the filter were measured after the drying process. The carbon mass balance was calculated based on the amount of raw material fed and gas produced and the amount of carbon captured.
After passing through the carbon capture filter, the gases were analyzed in the gas analysis section. The contents of hydrogen and methane were checked in real time using an online IR gas analyzer (A&D system 2000, A&D system, Seoul, Republic of Korea) and an FTIR analyzer (C1–C4 analysis, Gasmet DX4000, Gasmet, Vantaa, Finland). At the same time, the product gas was sampled and further analyzed for its composition of C1–C5 hydrocarbons via GC (gas chromatography, YL6500, Young Lin, Anyang, Republic of Korea). In addition, the flow rate of the generated gas was measured using a dry gas meter, and all measured values were collected and stored in real time with a data logger (GL840, Graphtec, Yokohama, Japan) and used to organize the experimental results.
A detailed description of the experimental apparatus and methods can be found in the existing literature [
14]. The main experimental variables and operating ranges of this study are summarized in
Table 1.
The main factors to evaluate the performance of the methane plasma reaction can be defined as follows.
where
and
Pplasma represent plasma thermal efficiency and plasma power output, respectively.
where the yield of each component is based on the theoretical production of 2 moles of hydrogen and 1 mole of carbon per mole of methane, as shown in the reaction equation above.
where
represents energy efficiency, which is the ratio of the energy of product
i to the power energy supplied by plasma and the chemical energy supplied by methane.
LHV and
m refer to the lower heating value and mass flow rate of product
i and methane, respectively.
3. Results
3.1. Characteristics of Plasma Discharge
Plasma discharge characteristics such as plasma flame stability, plasma power, power loss, and thermal efficiency can be affected by the applied current and plasma transfer gas flow rate. To avoid the effect of plasma discharge space limitation, the plasma discharge characteristics were investigated in an open space, and the formation of plasma flames based on the discharge conditions is compared in
Figure 4.
As can be seen from
Figure 4a,b, under constant flow rate conditions, the formation of the plasma flame was found to become unstable as the applied current increased. However, as the flow rate increased (
Figure 4b,c), the size of the flame increased, and it appeared to maintain a stable shape. Generally, under certain power conditions of plasma discharge, as the applied current increased, the plasma transfer gas flow rate decreased, and the plasma flame length decreased accordingly. The length of the flame affected the thermal shock of the plasma torch electrode, and as the length became shorter, the thermal shock tended to increase. On the other hand, as the voltage was maintained at a high level, the transfer gas flow rate increased and the length of the plasma flame increased accordingly, thereby alleviating the thermal shock to the electrode.
The effects of applied current on plasma discharge power and power loss under a constant gas flow rate are shown in
Figure 5.
As the applied current increased from 20 A to 40 A, the voltage slightly decreased, but the plasma power increased from 6.7 kW to 10.2 kW at gas flow rate of 30 L/min and from 8.9 kW to 10.8 kW at gas flow rate of 40 L/min, thus reducing the overall plasma resistance. The reduction in plasma resistance is related to arc length and electrical conductivity. In this study, this can be understood as the effect of increasing electrical conductivity as the temperature increased, and the arc length at the fixed electrode can be considered to have been relatively constant. Additionally, as the current increased, the coolant outlet temperature increased compared to the relatively constant coolant inlet temperature. In addition, as the difference between the coolant inlet and outlet temperatures increased, the power loss, that is, the heat loss due to cooling water, also increased from 2.5 kW to 4.6 kW, accounting for about 45% of the total plasma power.
In addition,
Figure 6 shows the effect of the plasma transfer gas flow rate on the plasma power and power loss.
As the plasma transfer gas flow rate increased, the voltage and plasma power tended to increase relatively linearly. However, the difference between the coolant inlet and outlet temperatures decreased, and heat loss due to the coolant also tended to decrease to about 40% of the total plasma power.
As a result, the thermal efficiency of the plasma discharge decreased from 62.6% to 54.6% as the applied current increased but increased from 53.0% to 60.4% as the gas flow rate increased (
Figure 7).
This change in thermal efficiency of the plasma discharge is thought to have been due to the sensible heat transfer effect and the radiant heat transfer effect. As the plasma transfer gas flow rate increased, the sensible heat transfer effect of the gas increased, and as the flame length increased, the radiative heat transfer effect of the plasma flame increased, thereby increasing the plasma thermal efficiency. On the other hand, whereas the thermal efficiency of previously reported large-capacity plasma torches reached the level of 70–90% [
15,
16], the thermal efficiency of this study using a 10 kW pilot plasma torch remained at a relatively low level of 53–64%. This is believed to have been because the heat loss due to the cooling system was relatively large for the small pilot torch, and additional tests are planned for mid- to large-sized facilities.
3.2. Plasma Thermal Cracking of Methane
Methane thermal cracking experiments were carried out using two types of plasma reactors. As explained earlier, the only difference between the two reactors was the methane supply method, but the size of the reactors was the same.
Figure 8 shows the typical plasma discharge operation and product gas composition using the type A reactor. The results using the type B reactor showed a similar trend.
The plasma discharge output in the reaction chamber was reduced to about 2~4 kW due to space constraints, but it was confirmed that the discharge could be maintained stably. The gas generated during the methane thermal cracking process was cooled and then analyzed using an online IR gas analyzer. As the reaction progressed, the gas composition also remained relatively constant. In the case of small plasma facilities, the content of plasma transport gas is relatively large, and in this study, nitrogen as the plasma transport gas accounted for about 80% of the reactor outlet gas. Therefore, the product gas was evaluated on a N2-free basis. The product gas consisted mainly of hydrogen, accounting for about 70% on a N2-free basis, and the remainder consisted of unreacted methane (about 20%, N2 free) and hydrocarbons of C2 and higher (about 10%, N2 free). On the other hand, carbon oxides such as CO and CO2 were rarely generated, and the average composition was less than 1.6%. As a result, it was confirmed that turquoise hydrogen could be produced through this process.
3.2.1. Effect of Methane Feed Rate
The effect of the methane feed rate on methane thermal cracking was investigated using a type A reactor under constant power conditions to exclude plasma flame mixing effects. The type A reactor, unlike the type B reactor, maintained a certain distance between the plasma flame and methane feed port to prevent damage to the feed port due to plasma flame disturbance based on the methane feed rate. The changes in the flow rate and composition of methane thermal cracking gas products with methane feed rate are shown in
Figure 9 on a N
2-free basis.
As the methane feed rate increased, the product gas flow rate tended to increase relatively linearly due to the increased methane supply. On the other hand, the composition of the product gas indicates that the methane content increased, whereas the hydrogen content decreased as the methane feed rate increased. This is because the increased methane feed rate under constant plasma output conditions led to a relative decrease in reaction factors such as mixing and heat and mass transfer. As a result, unreacted methane increased, and the methane conversion decreased (
Figure 10).
Methane conversion reached up to 57.8% at the low methane feed rate and decreased to 9.8% as the methane feed rate increased, which also reduced the hydrogen yield to 16.4%. However, hydrogen production increased due to an increased methane supply.
The effect of the methane feed rate on the energy efficiency of the hydrogen and gaseous product production is shown in
Figure 11.
As the methane feed rate increased, the energy efficiency of the hydrogen production decreased slightly, with an average efficiency of approximately 6.8%. On the other hand, the energy efficiency of the product gas, including unreacted methane and other hydrocarbons, increased to approximately 65%. Energy loss resulted from sensible heat loss of the product gas and cooling water, as well as loss due to solid carbon production. Under constant plasma power conditions, the sensible heat loss can be maintained at a relatively constant level. However, as the methane feed rate increased, solid carbon production tended to decrease to around 5.8%, as shown in
Figure 11b, and energy loss due to the solid carbon also tended to decrease accordingly.
3.2.2. Effect of Plasma Power
The effect of plasma power on the methane thermal cracking reactions was investigated under constant methane supply conditions to exclude the effect due to changes in methane flow rate. To confirm the mixing effect as well as the thermal effect based on the plasma power, a type B reactor capable of supplying methane close to the plasma flame was used. The changes in flow rate and composition of methane thermal cracking gas products with plasma power are shown in
Figure 12 on a N
2-free basis.
Under constant methane feed rate conditions of 3 L/min and 5 L/min, as the plasma power increased to 3.3 kW and 2.8 kW, the product gas flow rate increased slightly, averaging 4.0 L/min and 6.2 L/min, respectively, on a N2-free basis. In addition, as the plasma power increased, the unreacted methane content in the product gas decreased, whereas the hydrogen content increased, reaching 84.9% and 57.1% on a N2-free basis, respectively. The average content of the hydrocarbons above C2 remained almost constant at approximately 9% and 18% on a N2-free basis, respectively, depending on the methane feed rate. As with the results of a type A reactor, carbon oxides were also not detected in the gas produced from the methane thermal cracking reaction using a type B reactor.
The changes in methane conversion and hydrogen yield according to plasma power are shown in
Figure 13.
As the plasma power increased to 3.3 kW and 2.8 kW, the reduction in unreacted methane led to an increase in methane conversion to approximately 95% and 67% at the methane feed rates of 3 L/min and 5 L/min, respectively. In other words, as the plasma output increased by 40%, the methane conversion rate increased by 50% and 26% depending on the methane supply conditions, resulting in correlation coefficients of approximately 1.3 and 0.6, respectively. The increase in methane conversion is believed to have been due to improved mixing and heat and mass transfer effects as the plasma power increased. As a result, hydrogen production and yield also tended to increase.
Figure 14 shows the energy efficiency of the hydrogen and gaseous products production and the yield of solid carbon as a function of the plasma power.
As the plasma output increased to 2.7 kW, the energy efficiency of the hydrogen production tended to increase due to the increase in hydrogen production. However, when the plasma power increased to 3.3 kW, the increase in energy efficiency was offset by the increase in energy losses due to the increased energy supply, and thus the energy efficiency of hydrogen production stagnated or decreased slightly. On the other hand, the energy efficiency of gaseous products, including hydrogen, unreacted methane, and hydrocarbons, tended to decrease when increasing the plasma power, and it is believed to mainly have been due to the production of solid carbon. The increased methane conversion with increasing plasma power caused an increase in solid carbon yield, and the chemical energy and heat of the solid carbon was excluded from the energy efficiency evaluation.
3.2.3. Effect of Methane Supply Method
The effects of plasma flame mixing were examined by comparing the methane thermal cracking reaction characteristics based on the methane supply method under constant conditions of a methane supply amount of 3 L/min and a plasma output of 3.3 kW, and the main comparison results are summarized in
Table 2.
Under the conditions of an almost identical plasma power and methane feed rate, the gas flow rate produced by the type B reactor was slightly increased compared to that of the type A reactor. On the other hand, as the unreacted methane decreased by 93%, the methane conversion in the type B reactor increased by more than twice that of the type A reactor. As a result, hydrogen and solid carbon yields increased by 79% and 140%, respectively. The improvement in reaction efficiency is believed to have been the result of rapid heat and mass transfer due to the high-temperature flow phenomenon by injecting the methane close to the plasma flame in the type B reactor compared to the type A reactor. Additionally, recent results from catalytic methane decomposition (CDM) processes are compared in
Table 2. In the case of catalytic processes, the average value of recent results is compared because there is a large difference in conversion and yield depending on the type of catalyst used and operating conditions. The average methane conversion and hydrogen yield of the previous CDM processes were 64% and 50%, respectively, so the reaction efficiency of the type B reactor was evaluated as being relatively excellent. When the solid carbon productivity of the existing literature was adjusted according to Equation (4), the average carbon yield was about 51%, which is in a range similar to that of the results of this study.
In addition, the energy efficiency based on the total gas products and hydrogen production is compared to other processes in
Table 3.
The energy efficiency of this study was evaluated as being relatively low compared to that of other processes such as water splitting and conventional conversion processes, and this is believed to mainly be the result of reduced plasma thermal efficiency and solid carbon production. As mentioned earlier, by using a small lab-scale plasma facility, the plasma thermal efficiency was found to be lower than that of a bench or demo-scale facility, and the heat losses can be reduced through process scale-up and optimal design.
In addition, the energy supplied through methane and plasma was converted and distributed into sensible heat and chemical energy of gas and solid products through the reactions. Unlike conventional processes that convert supplied carbon into gaseous products, this process recovers carbon components in the form of solid products. The solid carbon conserved approximately 13% (type A) and 31% (type B) of the raw material energy, which is consistent with previous findings [
14]. Accordingly, the energy distribution of the gas product was reduced, and the energy efficiency of the generated gas was evaluated as low for the energy distributed in the solid carbon. As a result, the process can be made more competitive by converting solid carbon into high-value products.
3.3. Characteristics of Solid Carbon
The solid carbon generated by methane plasma thermal cracking reactions was recovered from the carbon filter of the downstream gas discharge line after completion of the reaction, and the carbon deposited on the inner wall was also be recovered after dismantling the reactor. The SEM image and XRD analysis results of the solid carbon recovered from the carbon filter (CA) and the carbon deposited on the inner wall near the plasma flame outlet (CB) are compared in
Figure 15.
The carbon sample collected from the plasma flame outlet showed a more agglomerated form compared to the carbon sample recovered from the carbon filter. In addition, both of the solid carbon samples had a largely rounded shape with carbon nodules stuck together, like the morphology of fresh carbon black [
22]. Additionally, as previously reported [
23], high-purity carbon components were confirmed through SEM-EDX analysis of carbon samples. Meanwhile, the XRD analysis results showed different peak characteristics depending on sample recovery location. The results of carbon samples recovered from the plasma flame outlet (CB) showed sharper and more intense peaks compared to the peaks of carbon recovered from the reactor outlet, and these peak characteristics can be observed in carbon black that has undergone a high-temperature heat-treatment process [
24]. Heat-treated carbon black can uniformly improve physical characteristics such as surface homogeneity, stability, and electrical resistance properties, which affect product quality and performance, so it can be used in a variety of fields [
25].
4. Conclusions
In this study, methane thermal cracking experiments were carried out using a DC arc plasma torch. The main product of this process is turquoise hydrogen without CO2 generation. In addition, solid carbon as a byproduct can also be used as a valuable chemical.
As a result of preliminary tests on the plasma discharge characteristics, it was possible to induce a stable operation by increasing the high voltage and plasma transfer gas flow rate, and it is believed that damage to the plasma electrode can be reduced under these conditions. In the methane thermal cracking experiments, stable discharge was confirmed by controlling the plasma power in the range of 2 to 4 kW. The experimental results show that the hydrogen yield decreased to 16.4% as the methane feed rate increased. On the other hand, under conditions where the methane feed rate was kept constant, the methane conversion increased with increasing plasma power, resulting in an increase in hydrogen yield to 58.8%. The yield of hydrogen and methane conversion was also greatly affected by the methane supply method. Under the condition of supplying methane close to the plasma flame, hydrogen yield and methane conversion increased by approximately 79% and 160%, respectively. In addition, the change in solid carbon yield based on the methane feed rate and plasma power showed a similar trend to the hydrogen yield, and the solid carbon yield was also found to increase to 62.9% under the condition of maximum hydrogen yield.
Solid carbon materials are used for various purposes in various fields, such as the rubber industry, the ink and paint industry, electrical conductors, the plastic and textile industry, etc. Through this process, high-purity solid carbon can be recovered, and carbon with high-temperature heat treatment characteristics can also be recovered in the plasma flame area. Additionally, the recovered carbon can be used to manufacture graphene, which is used as a high-tech industrial material, via further purification and upgrading processes. As a result, with process optimization based on the intended use of the final product, it is possible to produce not only clean hydrogen but also high-purity solid carbon that has various uses as a chemical product. Commercialization of recovered carbon is as important as producing and utilizing clean hydrogen, which can strengthen the competitiveness of this process compared to existing processes.