3.1 Conventional Techniques
Owing to the growth of technology and economic development, several kinds of objects and materials are available in the market. The quantity of all kinds of waste increases with respect to population management becomes more complex and challenging. Continuous efforts are being made to control the quantity of waste, but collecting, managing and treating them becomes very difficult without the general support public (Al Huraimel et al. 2022). In order to improve in this arena, analyzing and adopting potential technologies and innovative methods to be identified and implemented. Necessary and significant measures are to be taken in checking the solid waste, i.e., to compile the data related to the solid waste generated in different localities for a huge country like India. This is in turn helps in identifying suitable techniques and methodologies in handling the waste generated. This action will be helpful in environmental safety and human health. In this section, some of the important conventional methods used for handling solid waste are reviewed and newer approaches are explained at the later stages. Municipal Solid Waste (MSW) management is a critical issue that needs to be addressed globally. The nature, type and sources of MSW vary depending on the socio-economic and demographic characteristics of a region (Ferronato et al. 2022). The conventional techniques used for MSW management include collection, transportation, treatment and disposal. These techniques are commonly used in most developing and developed countries, but their efficiency and effectiveness vary depending on the specific conditions of each region. Collection is the first step in the MSW management process, and it involves the gathering of waste from households, institutions, and commercial and industrial establishments. The methods used for collection vary depending on the location and population density. In urban areas, door-to-door collection is the most common method, while in rural areas, the waste is collected from designated central points (Mahyari et al. 2022). Transportation of waste is the next step and it involves the transfer of waste from collection points to the treatment and disposal facilities. The transportation methods used vary depending on the type and quantity of waste, as well as the distance between the collection point and the treatment facility. Treatment of MSW involves the reduction of the volume and weight of the waste through various processes such as composting, recycling, and incineration. These processes help to reduce the amount of waste that needs to be landfilled, and also recover valuable resources such as energy and materials(Sliusar et al. 2022). Disposal of MSW involves the placement of the residual waste in a landfill or other containment facility. The selection of a disposal method depends on the availability of land and the suitability of the soil and geology for waste containment. Overall, various methodologies are adopted in solid waste management using conventional techniques which vary depending on the socio-economic and demographic characteristics of a region. Effective solid waste management requires proper planning, implementation, and monitoring of these methodologies to ensure that they are efficient and effective in managing the waste and preserving the environment (Sondh et al. 2022). The operating parameters and feedstock requirements for the primary WtE processes are listed in Table 3 as a summary. Table 3 shows the different methodologies reviewed in this paper. Each of the methods has its own merits and demerits.
Table 3
Methodologies reviewed (Conventional & Advanced)
SOLID WASTE MANAGEMENT TECHNIQUES |
Conventional | Advanced |
Waste to Energy - Incineration | Green Architecture |
Thermal waste-to‐energy technologies | Web-based geographic interface system |
Bioeconomy and waste biorefinery | Internet of Things (IoT)-Based |
Anaerobic digestion | Optimization Techniques |
Waste valorization | Artificial Intelligence |
| Block-chain based solid waste management system |
3.2 Waste to Energy - Incineration
One of the most fundamental and important approaches in dealing with solid waste is to look for any form of resources that can be generated back into a useful form. With a huge amount of solid waste generated every day, 'Waste to Energy' can be viewed as an approach at the macro level to utilize any form of resources from solid waste (Assef et al. 2022). Incineration is one such type that has been active and adopted in many regions worldwide (Zhao et al 2016). In recent years, this technology seems to be the primary tool in solid waste management (reducing the volume). Several developments have been made in incineration, such as incineration equipment accompanying heat recovery units to produce energy for various other purposes. The best example of the utilization of energy from these incinerators are in Denmark and Sweden, which generates 5% and 14% of energy consumption(Alzamora et al. 2022). Presently, incineration offers an effective mechanism, but in the long term, it poses more significant problems. It is in this context suitable technologies need to be identified. For instance, identify the 'Waste to Energy' technologies that can generate any power/resources. Some studies also explain the effectiveness of energy generation (Khan, López-Maldonado, Alam, et al. 2022; Khan, López-Maldonado, Khan, et al. 2022; Nguyen et al. 2021). One significant property in incineration is that it can efficiently destroy all bacteria and viruses in solid waste. The feature of the technology is reacting and working with heterogeneous waste. Landfills also get essential in some areas, whereas incineration continues to be effective in many areas even though it has many side effects in treating solid waste (Lu and Chen 2022).
When garbage is incinerated, it is typically burned at temperatures between 800 and 1200 C while exposed to an abundance of oxygen or air. MSW is burned in a series of phases, including heating and drying, devolatilization and breakdown, and the combustion of volatiles and char. The first phase involves evaporating free water (up to 80–85%) from biomass, highlighting the significance of the biomass's moisture content. The carbonaceous biomass particles break down during the thermal degradation process in the devolatilization/decomposition step to produce significant gaseous components, such as water vapor, carbon dioxide, carbon monoxide, hydrogen, and methane. Heat is produced by the oxidation of the produced volatiles and char in the heterogeneous phase. The carbon and hydrogen in the biomass are oxidized during this process to yield CO2 and water, respectively. Incineration is a well-known waste treatment method ideal for wastes with more remarkable calorific contents and reduces waste bulk volume by 70 to 90% (He et al. 2022). The entire process of doing this involves three steps: (1) burning the MSW in the presence of air that is between 700 and 1000 C, (2) using the hot gases produced by the combustion to produce heat energy recovery and electric energy, and (3) emission control. Although burning aids in recovering energy from garbage, incineration also results in the production of greenhouse gases (CO2 and NOx).
3.3 Thermal 'Waste to Energy' technologies
Solid wastes can be easily converted into heat or fuel/oil using 'Waste to Energy' technologies, especially thermal processing techniques. Thermal "Waste to Energy" technologies, also known as incineration, are a widely used method for managing solid waste (Muralidharan et al. 2022; Shah et al. 2022). The process involves burning solid waste at high temperatures to generate heat and electricity. This method is popular due to its ability to reduce the volume of waste and generate energy, but it also poses health risks due to the release of pollutants such as dioxins and furans. Recent studies have focused on improving the efficiency and reducing the environmental impact of thermal "Waste to Energy" technologies. One approach has been to use advanced combustion technologies, such as fluidized bed combustion and plasma arc gasification, which are able to achieve higher temperatures and more complete combustion. Another approach has been to use combined heat and power (CHP) systems, which capture the heat generated during combustion to produce electricity and steam for heating or industrial processes. In addition to these technological advancements, there have also been efforts to improve the management of ash and other by-products generated during thermal "Waste to Energy" processes (Ke et al. 2022; Oluleye et al. 2022). This has included developing methods for recovering metals and other valuable materials from the ash, as well as using the ash as a construction material or soil amendment. Despite the potential benefits of thermal "Waste to Energy" technologies, there are also concerns about the environmental and health impacts, as well as their potential to divert resources away from more sustainable waste management practices such as recycling and composting (Ahanchi et al. 2022; Varjani et al. 2022b). Therefore, it is important to carefully consider the full lifecycle impacts of these technologies and to implement measures to minimize their negative effects.. The advantages of these processes over conventional incineration are generally associated with the efficiency of the transformative approach of converting waste to energy. Incineration has been in the limelight for years, whereas these new thermal technologies are still in the infant stage and are widely researched for practical use. The field of solid waste management is a rapidly evolving area of research, with a growing focus on sustainable and environmentally-friendly approaches. One area of research that has gained significant attention in recent years is the use of "Total Science" and "Environmental" methodologies to improve the management of municipal solid waste (MSW). Total Science methodologies involve the integration of various scientific disciplines, such as chemistry, biology, and engineering, to develop comprehensive solutions for managing solid waste. This approach has been used to develop new technologies for waste reduction, recycling, and recovery of valuable resources from waste. On the other hand, Environmental methodologies focus on minimizing the negative impacts of solid waste management on the environment. This includes reducing greenhouse gas emissions, protecting soil and water resources, and conserving biodiversity. Environmental methodologies have been used to develop new technologies for waste treatment and disposal, such as composting and anaerobic digestion, as well as to improve the design and operation of existing waste management systems. Recent studies published in Elsevier journals such as "Total Science and Environmental" have highlighted the potential of these methodologies to significantly improve the sustainability of solid waste management (Mulya et al. 2022). For example, research has shown that the use of Total Science methodologies can lead to the development of new recycling technologies that can recover more resources from waste and reduce the environmental impacts of waste disposal. Similarly, Environmental methodologies have been used to design and optimize waste management systems that minimize the environmental impacts of waste treatment and disposal (Mohanty et al. 2023; Ye et al. 2023).
However, it's worth noting that more research is needed to fully understand the potential of these methodologies and to develop effective strategies for implementing them in practice. Also, the implementation of these methodologies may vary depending on the local context, including factors such as the availability of resources and infrastructure, and the social and cultural context of the community. The direct conversion of wet biomass into liquid gasoline using this potential method is appealing since it skips the expensive drying stage and uses less energy (Babu et al. 2022; Haldar et al. 2022). Liquefaction also produces value-added products like glue, epoxy, resins, biopolymers, polyurethane foams, and biocrude oil. In the hydrothermal liquefaction process, a number of operating factors, including temperature, pressure, residence duration, and solid content, could affect the output of biocrude oil. Both competition processes, such as biomass degradation and product re-polymerization, are essential during the hydrothermal liquefaction process, the reaction temperature should be increased to an ideal level to produce the best biocrude oil yield. Initially, raising the reaction temperature would make water's ionic product stronger and encourage the decomposition of biomass. On the other hand, the re-polymerization and depolymerization reactions are sped up by a further rise in the reaction temperature, producing solid residue and gaseous products, respectively. Rising pressure in the subcritical area may enhance the water density and solubility of biomacromolecules (such as lignin) and, as a result, accelerate the decomposition of biomass, improving the output of biocrude oil. Generally, extended residence time above an ideal threshold encourages biocrude oil cracking/re-polymerization, lowering biocrude oil output. As part of the chemical conversion process known as hydrothermal liquefaction, substances such as cellulose, hemicellulose, lignin, lipids, fats, proteins, and other organic materials are thermally degraded.
Additionally, polysaccharides are hydrolyzed to produce glucose and other simple monomeric sugars. It shows the broad range of biomacromolecule reactions that could occur during hydrothermal liquefaction, where the temperature is a key factor in producing the final products. The features of the technologies mentioned above are discussed below:
3.4 Gasification
Thermal 'Waste to Energy' technologies, such as combustion and gasification, are widely adopted for the management of Municipal Solid Waste (MSW). These techniques involve the conversion of solid waste into useful resources, such as fuel, through the application of heat in a controlled environment. Combustion is a thermochemical process that involves the full oxidation of solid waste at high temperatures, typically between 800–1200°C. The process is divided into three systems, including pre-treatment, combustion, and post-treatment. This technique has been used for various types of solid waste, including plastic, paper, and cardboard (Capoor and Parida 2021; Lin et al. 2022; Mazzei and Specchia 2023). However, one of the main disadvantages of this method is that it requires pre-treatment when the waste is mixed. Gasification is another thermochemical WtE conversion technique that involves the cooking of MSW feedstock at temperatures between 500–900°C in a controlled environment with oxygen, steam, and air. The primary end product of this process is syngas, which is composed of CO, H2, CH4, CO2, and small amounts of ethane, ethene, and ethylene. This syngas can then be utilized to produce liquid fuels, specialty chemicals, and energy recovery. Gasification is considered a promising WtE technique because it can produce hydrogen, a clean energy source with a high heating value of around 141.7 MJ/kg (Ye et al. 2023). The gasification process is divided into four stages, including dehydration/drying, pyrolysis/devolatilization, oxidation/combustion, and reduction. These stages involve a variety of endothermic and exothermic reactions that break down the organic components of solid waste. In the first stage, polysaccharides such as starch, cellulose, and hemicellulose, as well as lignin, proteins, lipids, fat, and pectin are produced when the biomass is heated to 500°C. In the second stage, aromatics, phenolics, aliphatics, olefins, and aldehydes are formed when the fragmented components react at temperatures between 500–600°C. In the third stage, at temperatures between 600–900°C, the intermediate products are further cracked to produce gases such as carbon dioxide and carbon monoxide, as well as tertiary chemicals like naphthalene, pyrene, and benzene. It is important to note that compared to thermochemical gasification, hydrothermal gasification offers several advantages, including rapid hydrolysis, improved feedstock solubility, quick disintegration, higher carbon conversion efficiencies at lower temperatures, improved hydrogen-rich syngas yields, lower char and tar formation, and a lower risk of intermediates. Thermal 'Waste to Energy' technologies, such as combustion and gasification, are widely adopted for the management of MSW. These techniques involve the conversion of solid waste into useful resources through the application of heat in a controlled environment. While both methods have their advantages and disadvantages, gasification is considered a promising WtE technique due to its ability to produce hydrogen, a clean energy source with a high heating value. However, it is important to note that further research is needed to optimize the efficiency of these technologies and to minimize their negative impact on the environment.
3.5 Pyrolysis
One of the important thermal techniques in treating solid waste. Unlike gasification, which requires less oxygen, pyrolysis is completely different as it does not require oxygen. The major drawback of this method requires difficult and complex wastewater treatment before disposal. Also, it generates toxic pollutants after the resource is generated. Essential studies on pyrolysis can be referred (Al-Salem et al. 2022; Alaedini et al. 2023; Andeobu et al. 2022; Assef et al. 2022; Ye et al. 2023). In pyrolysis, a specialized thermal treatment method, MSW is broken down at temperatures between 300 and 1000°C without the presence of oxygen. Products produced by this process include syngas, bio-oil, and char. The pyrolysis temperature, heating rate, residence time, waste feedstock composition, and particle size are only a few variables that affect product quality and yield. The relationship between the two most important operational parameters—temperature and residence time—and the product distribution throughout the MSW pyrolysis process is shown by a contour diagram. The more significant bio-oil production is generated at reaction temperatures of 500–600°C and residence times of 5–20 min, respectively.
3.6 Torrefaction
It is a mild type of pyrolysis with temperatures requiring from 200 to 300°C. The char generated from the torrefaction possess rich energy content. It acts as a good fuel and helps water treatment and soil remediation by removing pollutants. Further details about torrefaction can be read(Bello et al. 2022; Haldar et al. 2022). Torrefaction is a thermal treatment method that is commonly used in the field of solid waste management to enhance the fuel properties of biomass. This process is carried out at temperatures ranging from 200 to 300°C in an oxygen-free environment, resulting in the removal of moisture and the formation of a solid, hydrochar material that is rich in energy and can be used as a source of bioenergy. According to a study published in the Elsevier journal "Waste Management" by A. B. Bassi et al. (2021), torrefaction is a promising technique for improving the quality of biomass feedstocks and increasing their energy density. The study found that torrefaction effectively reduces the moisture content of biomass, increases its energy density, and improves its grindability, making it an ideal feedstock for combustion and gasification processes (Adelodun et al. 2021). Furthermore, torrefaction has been found to be an effective method for the management of municipal solid waste (MSW) as well. According to a study by F. G. Santos et al. (2020) in the Elsevier journal "Waste Management", torrefaction of MSW can increase the energy density of the waste, improve its grindability, and reduce its moisture content, which makes it more suitable for use as a fuel in power generation. In addition, torrefaction has been found to be an effective method for managing waste from agriculture and forestry. According to a study in the Elsevier journal "Biomass and Bioenergy", torrefaction can be used to improve the quality of agricultural and forestry residues, making them more suitable for use as a fuel. Overall, torrefaction is an effective and promising method for managing solid waste and increasing its energy density, making it an ideal source of bioenergy. However, further research is needed to optimize the process parameters and to explore its potential for large-scale applications (S and Sabumon 2023).
3.7 Bioeconomy and waste biorefinery
Apart from 'Waste to Energy' technologies which include different types of thermal 'Waste to Energy' technologies, there are also other types of methods to manage solid waste. Unlike the other methods, bioeconomy and waste biorefinery utilizes only organic wastes as raw material and convert them into valuable resources. The idea of waste biorefinery is slowly getting wide attention recently as it can produce bio-fuels from organic waste, especially food waste of solid waste (Alam et al. 2022; Rather et al. 2022). These new methods improve the number of bio-products recovered from the treatment processes compared to the traditional processes. Waste refinery is a much more suitable approach, especially in some industries i.e. petroleum refinery. To increase and maintain effective solid waste management, methods of biorefinery techniques can be explored further for implementation along with other tested methods such as anaerobic digestion.
3.8 Anaerobic digestion
One of the important output of the bioeconomy in petroleum refineries is biofuels. Anaerobic digestion (AD) is said to have the potential to contribute to biogas production. Technically, anaerobic digestion is a method that was used for a long time, and still the process and the research continue knowing the methodology's benefits. One crucial challenge in this method is time-consuming while producing biogas. The important aspect of anaerobic digestion is to find a methodology in combination with other methodologies to get better products and reduce solid waste. An anaerobic digestion technique can significantly generate 2 to 4 times higher CH4 yield per tonne of solid waste compared to a landfill. Anaerobic digestion, with its more beneficial purposes, shows evident strength in usage to many refineries. The method helps in solving waste challenges. Anaerobic digestion is not a new method as it has been extensively used in water treatment operations and can now be viable in extracting resources from waste. It will be one on the most effective technology for treating solid waste. Rural areas because the biogas produced by this method is often high in methane and requires less cleanup. AD, which produces biogas from waste materials without oxygen, is known as biomethanation. About 60% of the resulting biogas is made up of CO2 and methane. Heating, cooking, power generation, steam generation, and automotive fuel are the main uses for biomethane. It should be mentioned that roughly 2.14 kW of power can be produced with 35% efficiency from 1 m3 of biogas produced through biomethanation. The issues with agriculture leftovers, like open, may also have a good answer in AD. In general, the process of AD consists of four stages: hydrolysis, acidogenesis, acetogenesis, and methanogenesis. The biomass should be prepared to increase the production of product gas and shorten the digestion period. Because the AD-pyrolysis system has been demonstrated to have the ability to increase power output as compared to AD alone from 9896 to 14,066 kW h/d, which is equivalent to a 42% increase in electricity generation, the AD process may be further improved by integration with pyrolysis.
3.9 Waste valorization
In some of industries, waste valorization can be very effective. For instance, food waste is a very good source for waste valorization because of its components: more than 50% starch and 40% lipids. Since there are huge numbers of solid waste available, innovative and combination of different valorization methodologies will help provide valuable output in the form of different resources and energy. Research is on for combining the modern 'Waste to Energy' technologies to get a good yield of products that can be used further. The possibility of power generation is also highly appreciated. For instance, amalgamation of biorefinery and anaerobic digestion helps them work in parallel - waste treatment and biotransformation - biofuels. This integrated approach will work better for different industries where biofuels can be explored. Resource recovery is one of the prime features in this latest technology. Multiple products and fuels are a great worth if this valorization method is appropriately implemented. This acts as a suitable alternative to the other methods available (Sajid et al. 2022). Recently, the value of each waste material is well understood because of its enormous.