Municipal solid waste (MSW) represents the waste generated daily by people, known for its widespread occurrence and intricate composition. The significant increase in waste production can be attributed to the processes of urbanization and industrialization. The practice of mass burn incineration has traditionally been a prominent thermal method for managing MSW [
1,
2]. There are more than 1400 operational incineration facilities globally, and many more are in the process of being commissioned for waste-to-energy applications [
3]. However, the overall energy efficiency of contemporary incineration plants remains relatively low, typically falling within the range of 22% to 25%. This is primarily due to the necessity of maintaining lower steam temperatures, usually around 450°C, to safeguard equipment from corrosion induced by acidic gases like HCl [
4]. Consequently, the demand for excessive airflow constrains the achievable temperature within the incineration process chamber, leading to the production of hazardous pollutants, including chlorinated dioxins and furans. These contaminants contribute to air pollution and are linked to severe health concerns such as cancer and developmental abnormalities [
5]. Despite the incorporation of state-of-the-art technologies for environmentally friendly waste disposal in modern incineration plants, the potential for generating toxic gases remains a subject of debate [
6]. The highest likelihood of dioxin formation occurs within the temperature range of 350 to 400°C [
7]. To address the negative environmental impacts associated with incineration, alternative technologies like pyrolysis and gasification have emerged as practical options. These methods have demonstrated their ability to reduce the generation of dioxins and furans to acceptable levels [
8]. Among these alternatives, gasification is considered more efficient for large-scale waste disposal. However, it does produce unwanted byproducts, such as tar, in addition to desired outcomes like syngas, producer gas, and char [
9]. The presence of tar in the product gas can lead to various adverse effects, including diminished product quality, fouling of pipelines, corrosion, and deactivation of catalysts [
10]. In this context, thermal plasma technology stands out as the singular thermal waste treatment process capable of effectively managing diverse waste types, including hazardous materials, while converting waste into valuable products without harming the environment [
11]. It offers a range of advantages over conventional methods, which encompass exceptional destruction efficiency (with volume reduction surpassing 99%), the removal of harmful molecules, decreased CO
2 emissions, and the production of high-calorific value gas [
12,
13]. By virtue of its high-temperature heat source and the presence of charged particles, plasma fosters increased reactivity within the environment. This, in turn, promotes the decomposition of tar and augments the rate at which tar is eliminated [
14,
15]. The adoption of thermal plasma technology has been on the rise and is being implemented in countries such as the UK, USA, Canada, Belgium, and India, where it serves as a waste-to-energy solution for electricity generation, with capacities reaching up to 100 MW [
16]. The realm of plasma-assisted waste processing technology is broadly categorized into two methods: plasma pyrolysis and plasma gasification. In plasma gasification, waste is subjected to a controlled quantity of oxygen, while plasma pyrolysis involves decomposing waste in an oxygen-deprived environment [
5,
12,
17]. In the context of thermal treatment, an air supply of less than or equal to 5% relative to stoichiometric air can be considered to lead to pyrolysis conditions for waste treatment [
18]. Numerous studies, ranging from laboratory to pilot-scale, have been conducted to explore the environmental and output implications of employing plasma pyrolysis technology for waste management. A wide array of waste materials, including polyethylene, polypropylene, rubber, tires, biomass, paper, refuse-derived fuel, and medical waste, have been treated using different power sources, such as DC, AC, RF, and Microwave, with power supply capacities ranging from 0.8 to 50 kW. In all instances, the primary composition of explosive products comprises H
2 and CO. The concentration of pollutants like CO
2 varies from 2% to 15%, while solid residues, taking the form of carbon black, slag, or ash, fall within the range of 6% to 40% [
19,
20]. Initially, it has reported that the eco-friendly treatment of medical waste using plasma pyrolysis technology necessitates an energy consumption of approximately one kWh per kg [
13]. Furthermore, Plasma Gasification Melting technology has been employed to convert MSW at a rate of 300 kg/h into syngas with energy content ranging from 6 to 7 MJ/Nm
3. In this process, steam feed rates vary from 70 to 100 kg/h, and plasma power consumption ranges from 0.8 to 0.87 kWh/kg [
21]. Stringent environmental regulations have created opportunities for plasma pyrolysis technology to emerge as a highly viable option for managing MSW and other solid wastes, ensuring minimal environmental impacts.
Thermal plasma refers to a high-temperature plasma operating at elevated pressures, typically close to atmospheric levels. It is characterized by high power and current densities within the plasma, resulting in significant enthalpy. This property allows thermal plasma to efficiently heat injected materials and electrodes. As a result of its exceptional heat capacity, thermal plasma finds widespread use in applications like arc welding, plasma arc cutting, waste disposal, and more. In some cases, thermal plasma can be generated not only between electrodes but also through inductive coupling, giving rise to what is known as inductively coupled thermal plasma (ICTP) [
22]. Reed originally developed the fundamental configuration of ICTP in the 1960s [
23]. It involves the establishment of plasma within a cylindrical dielectric tube encircled by an induction coil. Radiofrequency (RF) current flowing through the coil generates electromagnetic fields, which, in turn, accelerate electrons within the torch, thus creating plasma. When operating at high pressures, typically near atmospheric levels, the plasma assumes a thermal state, with gas temperatures reaching several thousand Kelvins, closely aligned with electron temperatures. One of the most significant advantages of ICTP is its ability to generate a clean, high-temperature environment free from contamination by electrode materials. Capitalizing on these benefits, ICTPs have found diverse applications, including waste disposal [
24], thermal barrier coating production [
25,
26,
27], diamond film deposition [
28], fullerene synthesis [
29,
30], fine powder spheroidization [
31,
32,
33], nanopowder synthesis [
34,
35,
36,
37], nanotube production [
38,
39], catalyst synthesis [
40], and astrophysical research [
41]. Despite the successful utilization of ICTP torches in numerous material processes, certain limitations have also emerged. These include challenges related to stable operation in the presence of disturbances, counterflows within the circulating gas, reduced power efficiency, and difficulties in controlling gas temperatures [
42].