Next Article in Journal
A Feasibility Study of Implementing IEEE 1547 and IEEE 2030 Standards for Microgrid in the Kingdom of Saudi Arabia
Previous Article in Journal
Composite Biochar with Municipal Sewage Sludge Compost—A New Approach to Phytostabilization of PTE Industrially Contaminated Soils
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Review

An Analysis of Circular Economy Literature at the Macro Level, with a Particular Focus on Energy Markets

by
Arezoo Ghazanfari
School of Economics, Finance and Marketing, RMIT University, Melbourne, VIC 3000, Australia
Energies 2023, 16(4), 1779; https://doi.org/10.3390/en16041779
Submission received: 22 December 2022 / Revised: 5 February 2023 / Accepted: 8 February 2023 / Published: 10 February 2023

Abstract

:
Sustainability is a strategic approach to develop a more sustainable economy to support the environment and socio-economic development. Literature on sustainability has been concerned mainly with global warming and environmental degradation issues, whereas the Circular Economy (CE) concept has recently been suggested as an alternative solution to support market sustainability and deal with both environmental and socio-economic challenges. In order to tackle these challenges, countries must switch from linear economies that follow the “take-make-dispose” principle to circular and sustainable economies. This study applies a structural and conceptual literature review to elucidate the most decisive determinants in the formation of circular strategies, particularly in the context of the energy sector. This study examines obstacles that hinder CE adoption and formulates drivers and measures to overcome them. The strategic literature review shows that the circular approach is critical in achieving sustainable development. Circularity can be considered a novel and innovative approach to alleviating the contradiction between rapid economic growth and energy and raw materials shortages. The CE structure must be considered as a sustainable foundation to enhance economic growth by avoiding waste, preserving natural capital, managing resource scarcity, recycling materials, maximizing energy efficiency, and recirculating them into the economy. Analysis reveals that the circular system is a key pillar of sustainability, security, and efficiency in the energy sector. The sustainable energy transition requires incorporating the CE principles in the design process. It also revealed that both public and private sectors must move away from the linear paradigm towards circularity to achieve CE implementation.

1. Introduction

Since the 20th century, greenhouse gas emissions have been the primary driver of climate change and global warming, leading to various health and environmental issues. Aside from climate change, air pollution, respiratory diseases, food shortages, and wildfire outbreaks result from climate change caused by greenhouse gases. In light of this, global emissions have caused concern in all economies [1,2,3]. Several factors contribute to global emissions, including a sizeable simultaneous surge in population, consumption, and economic growth, which are associated with an increase in resource and land consumption and waste production [4]. Population growth will increase the demand for natural resources, specifically energy, raw materials, water, and fertile land. Environmental pressure increases dramatically as the demand for these resources grows [5,6]. Humanity’s irreversible effects on the earth could make it impossible for the next generations to enjoy high living standards, primarily due to global warming, biodiversity loss, and land degradation [7].
Electricity production is one of the sectors contributing significantly to greenhouse gas emissions. Approximately 60% of the world’s electricity is generated from fossil fuels, requiring a gradual shift towards a more secure, sustainable, and accessible energy system. As reported by the International Energy Agency (IEA), over 40% of all energy-related emissions come from electricity generation. Globally, fossil fuels emit approximately 34 billion tonnes of CO2 annually [8,9].
In order to mitigate environmental threats, countries should adopt green strategies to establish a modern, circular, and sustainable economy. To transition toward a sustainable low-carbon energy system, countries must switch from fossil fuels to renewable energy sources and improve their energy efficiency. Recently, the world has seen an acceleration of ambitions regarding energy transition and decarbonization, particularly in terms of achieving net-zero carbon emission targets. In order to achieve net-zero targets and energy-efficient development, all industries must modify their infrastructures, a process that will require large-scale reconstruction and retrofitting for a very high cost. Energy industries also need to be entirely redesigned and implement new technologies in the process of electricity production or industrial activities (i.e., batteries and solar photovoltaic (PV)). In addition, the linear decarbonization process only focuses on the reduction of emissions from energy production and renewable energy consumption, which are not sufficient to reach net-zero targets. The CE approach is recently on government agendas as an effective means to support sustainability, accelerate decarbonization, and facilitate energy efficiency [10]. Therefore, CE approaches are complementary to existing energy and decarbonization policies in enhancing the energy transition toward a clean environment. Creating resources from waste is one of the most effective ways to contribute to sustainable development. To reduce waste and emissions in energy transition policies, policy makers must consider CE principles in their energy transition guidelines.
Over the past century, linear economies have dominated industrial development [11]. In an economy based on linearity, natural resources are directly transformed into waste because of the way in which they are designed and manufactured [12,13]. The process is comprised of three phases: take, make, and waste [14]. There is, therefore, a great deal of waste produced in traditional and linear economies. In contrast, circularity is an excellent replacement for the linear economy to eliminate waste, maximize resource efficiency, optimize material consumption, take advantage of renewable resources, and continuously replenish natural resources [15]. In circular economies, raw materials are reused instead of being produced from scratch, and a closed loop can be employed to achieve this objective [16]. The electricity sector can benefit from the CE strategies when dealing with renewable energy like solar, wind, and bioenergy. Over the past decade, the CE has gained popularity in areas such as sustainability, energy efficiency, resource management, and productivity. Circular economies make efficient use of bio-based materials in many different ways as they cycle between the economy and the environment. Environmental concerns such as climate change, biodiversity loss, waste, and pollution can be alleviated through CE strategies.
In terms of energy market perspective and CE strategies, countries have the potential to produce electricity from biomass, biogas, wind, and solar or use energy store systems or portable batteries. New technologies are being developed to generate energy from waste in a circular manner. As traditional technologies and coal-fired power stations are replaced by infrastructures and new technologies, it is essential to apply CE principles to unlock waste’s resource potential and minimize its management challenges. For example, waste-to-energy (WtE) generation technologies have recently emerged and gained increasing attention. WtE technologies utilize waste to generate energy in the form of electricity or heat. Like other power generators that use thermal coal, oil, or solar, WtE plants use waste as a fuel to produce electricity. In these plants, the concept of energy from waste involves converting non-recyclable materials into energy through various methods, including thermal and non-thermal processes (combustion, gasification, landfill gas recovery, and anaerobic digestion). A WtE system contributes to a sustainable and circular economy in various ways. As one of the solutions to increase circularity in the energy sector, we provide an explanation of WtE technologies in this study.
The circular strategy has become one of the most popular research areas from various disciplines and hemispheres in terms of conceptualization, definitions, drivers, metrics, and sustainability. The literature mainly concentrates on specific industries like manufacturing [17,18], construction [19,20], supply chain [21,22], energy [23,24], fashion [25,26], and water industries [27,28]. However, this study goes a step further and examines all aspects of the CE, such as motivations, barriers, technologies, and requirements for switching from a linear to a circular system in the global market and also the energy sector. The aim of this paper is to identify factors that can hamper, encourage, facilitate, or stimulate the transition towards a CE system.
Using a systematic literature review and various perspectives of scientific studies, this paper explains what the circular economy is, why it is essential, what are drivers and barriers, and how it can be accelerated. Unlike the previous literature, which has discussed the background and concept of the CE itself, in this paper we examine current CE progress as well as the steps that need to be taken to accelerate its growth. In the first stage, an in-depth and general analysis is provided of corporate CE approaches and their applicability and transferability to the macroeconomic level across all industries. Then, a particular emphasis is placed on the energy sector to examine the implications of the CE system in the energy sector in terms of decarbonizing electricity generation and utilization, as well as its wider implications. We discuss principal drivers and obstacles to the implementation of CE approaches in a global context as well as in energy markets. We identify how the current scheme of policies could facilitate and incentivize CE measures to complement existing energy policies in order to achieve the full decarbonization target.
This article explores the potential for CE development in all industrial sectors through waste management strategies. Through a combination of literature review and computational models, we identify the main motivations and obstacles to the implementation of CE and propose significant solutions that policymakers and government officials should consider. It is revealed that CE approaches are very critical and effective solutions for economic growth, sustainability, and energy decarbonization, which are beneficial not just for energy markets but also for other industries. It shows that the CE contributes to the reduction of pollution, water acidification, and carbon emissions that ultimately contribute to climate change. Furthermore, this study illustrates how CE strategies can lead to a range of environmental benefits in the energy sector.
It has been discovered that there are many obstacles that have to be addressed in order to establish a circular system that is capable of bringing socio-economic and environmental benefits to the wider economy. There are practical barriers to the CE adoption in economies, including economic and financial obstacles, regulatory policies that are dominantly targeted towards traditional and linear economic models and hence linear decarbonization policies, knowledge barriers, cultural obstacles, and technical limitations. It is interesting to note that obstacles are interconnected. For example, the lack of CE policies reflects a lack of knowledge about the CE concept among regulators and legislators. Alternatively, consumer knowledge and awareness are reflected in regulators’ knowledge. It indicates that all aspects of society can contribute to the adoption and implementation of circular economic systems. Therefore, the first step in the transition from a linear to a circular economy is enhancing social knowledge about the importance and benefits of circularity.
The practical implications of this study can be represented as follows. First, circularity is frequently the subject of research among scientists and professionals. However, CE development requires the involvement of governmental bodies, policymakers, and stakeholders beyond the expert community in order to increase knowledge of CE necessity and its implementation. This paper will stimulate and motivate governmental bodies to invest in circular developments and bio-energy generators to reduce emissions. Second, circularity can be considered as a novel and innovative approach to alleviate the contradiction between rapid economic growth and shortages of energy and raw materials. Third, since eco-circular approaches are developed to enhance efficient resource allocation, CE approaches should remain applicable even once zero-emission targets are achieved. Fourth, we found that waste-to-energy technologies are the best alternative way to generate electricity from waste, which contributes to a sustainable and circular economy in a variety of ways. A waste-to-energy plant can produce electricity, heat, or fuel in the form of renewable and clean energy, resulting in fewer greenhouse gases and a smaller carbon footprint. Fifth, a clear public policy framework should be implemented by evaluating economic strategies, CE perspectives, and decarbonization policies simultaneously.
The remainder of this paper is organized as follows. We discuss the research design and framework of the study in Section 2. A conceptual analysis of the CE approach is presented in Section 3. Results are presented and discussed in Section 4, while the conclusion is summarized in Section 5.

2. Research Design

This section aims to identify the most relevant studies in the context of the CE. This study is certainly not the first on the topic of circularity, and a great deal of literature has already been published on the transition from a linear to a circular system. Previous studies focused on particular geographic locations or industries. In addition, they only focused on a few of the following concepts: motivations, challenges, technologies, practices, industries, and requirements. However, this study presents a comprehensive overview of all aspects of CE adoption in global markets. Accordingly, this paper aims to delve into the main motivations, obstacles, and requirements in implementing a CE at the macro level, with a particular focus on energy markets.

2.1. Framework of the Literature Review

An integrated systematic review was conducted in this study to evaluate different perspectives of the CE. Systematic reviews help identify trends and changes in a research area and track the evolution of knowledge about a specific topic [29]. This study is designed to achieve a comprehensive understanding of CE within both the global view and the energy transition concept. Significant objectives of this study are: (1) present a comprehensive review of the CE literature; (2) examine various aspects of circular economies, like advantages/disadvantages, motivations, barriers, and implementations; and (3) provide recommendations and solutions for accreditation of the CE. The framework of the literature review is presented in Figure 1.

2.2. Literature Review

In the first step, a structured keyword search is conducted across a variety of search engines to improve the reliability of the collected data, including Google Scholar, Science Direct, Willey, JSTOR, Taylor & Francis, PubMed, and IEEE Xplore, Scopus, and Web of Science. It must be noted that Google Scholar is considered the primary web search engine for the literature collection in this study. Other databases are considered for robustness checks to identify all relevant studies. However, Google Scholar provides access to all referenced studies.
Keywords like ‘Circular Economy’, ‘CE’, ‘Circularity’, ‘Circular’, ‘Circular System’, ‘Decarbonization’, ‘Energy’, ‘Renewable Energy’, and ‘Energy Transition’ are investigated. In CE notion, the following keywords are used: ‘Motivation’, ‘Driver’, ‘Advantage’, ‘Disadvantage’, ‘Obstacle’, ‘Barrier’, ‘Practices’, ‘Solution’ and ‘Recommendation’ are jointly found.
Considering the numerous potential benefits of the CE compared with the conventional economy, a large strand of literature has been undertaken to examine various features of the CE across a wide range of contexts. A variety of publications are examined to develop a comprehensive and robust study, including peer-reviewed articles, grey literature, PhD dissertation and books. From 2010 to 2022, more than 900 studies focused on circular economies across different sectors. There has been a particular focus on manufacturing, agriculture, construction, supply chain, energy, fashion, and water industries. These studies mainly focus on some specific areas, which are highlighted in a representative list in Table 1, along with some samples of studies. As shown in the table, supply chain, agri-food, energy, fashion, manufacturing, furniture, and water are the main spotlights of CE studies within these sectors.
Conducting a systematic literature review commences by determining which publications are worth considering and which should be excluded. More than 349 publications were collected, of which 52 publications are considered relevant to the research objectives since they study different aspects of the CE in the global markets and the energy sector. The division of the studies sheds light on the debate surrounding the CE within the scientific and practitioner communities. Figure 2 depicts the distribution of studies with a specific focus on circularity from 2010 to 2022. The figure shows that the number of publications in the CE context has increased significantly in the past decade.
Figure 3 presents the main characteristics of the sourced literature, including the most common geographical locations of CE studies and the distribution of literature in the energy sector. The distribution of studies based on geographical locations is presented in Figure 3a. As shown, China, European countries, India, Africa, and the United States are the most significant countries considered by scholars. China accounts for the majority of studies; 250 studies have been conducted there (23%). Figure 3b displays the contribution of energy studies from 2010 to 2022. Research findings reveal that fewer studies have conceptually examined circularity approaches in energy markets. The number of publications has increased significantly since 2016, indicating a growing interest in CE strategies in the energy sector.
At the end of the review process, a comprehensive assessment of all collected studies is conducted to find motivations, barriers, and requirements for switching from linearity to the circular economy and presents essential solutions.

3. Conceptual Analysis of Circular Economy

3.1. Global Review of Circular Economy

In the late 1970s, the concept of the CE gained momentum. It was introduced by Kenneth E. Boulding, who first mentioned it as an academic concept in 1966, criticizing linear “cowboy economies” and describing a future “spaceship economy” in which all used resources were redirected back into it [13,100]. The CE, derived from Boulding’s theory, was developed by the environmental economists Pearce and Turner [101] in which they discuss the lack of markets and prices for environmental goods and emphasize the need to internalize these costs. It is more likely that a transition towards a circular system will occur if these externalities are internalized [102]. There are several authors, including Andersen [103], Ghisellini et al. [13], and Su et al. [104], who give credit for the introduction of the concept to Pearce and Turner [105].
Some specific features of CE were introduced by Stahel and Reday [106], particularly in the field of industrial economics. In their conceptualization, a loop economy is used to describe industrial strategies for preventing waste, creating jobs, efficiently utilizing resources, and dematerializing the industrial system.
As stated by Ghisellini et al. [13], a circular strategy is an economic structure designed to improve resource efficiency and interaction between the economy, environment, and society. Accordingly, CE can be considered as a novel and innovative approach to alleviating the contradiction between rapid economic growth and shortages of energy and raw materials [107].
There have been several academic reviews about CE concepts, including those by Andersen [103], Su et al. [104], Sassanelli et al. [108], Kristensen and Mosgaard [109], De Pascale et al. [110], and Mhatre et al. [111]. There has been a particular focus on supply chains, sustainable business models, and circular product design.
The principles of CE are as follows: (1) enhance and preserve natural resources through the management and replenishment of natural capital; (2) make optimal use of materials and resources to maximize value; and (3) eliminate negative externalities from the economic system and lifestyles in order to promote system effectiveness [112,113].
Over the past two decades, the CE has gained momentum among policymakers, influencing national, regional, and local governments, as well as inter-governmental agencies. Germany has been a pioneer in the incorporation of the CE into national laws. In 1996, Germany passed the CE and Waste Management Act (also referred to as the Circular Economy Act or the “KrWG”) that explicitly promoted the concept of CE [114]. In January 2002, this was followed by Japan, which established a comprehensive legal framework, titled Japan’s 2002 Basic Law, to achieve a recycling-based society [104,115,116]. Another country was China, which introduced the “Circular Economy Promotion Law of the People’s Republic of China” in January 2009 [117]. Figure 4 is a graphical scheme of a cyclical pattern in a circular economy.

3.2. Waste to Energy

Millions of tons of waste are constantly produced and dumped in landfills, which adversely affects ecosystems, the environment, and the health of humans and wildlife. New technologies are being developed to generate energy from waste in a circular manner. Waste-to-energy (WtE) is the process that uses waste to generate energy in the form of electricity or heat. Like other power generators that use thermal coal, oil, or solar, WtE plants use waste as a fuel to produce electricity. In these plants, the concept of energy from waste involves converting non-recyclable materials into energy through various methods, including thermal and non-thermal processes (combustion, gasification, landfill gas recovery, and anaerobic digestion). Economies are striving to develop technologies for compressing and disposing of waste while also generating energy from it. The energy that is produced in the form of electricity, heat, or fuel using WTE plants is renewable, clean, and environmentally friendly, producing fewer greenhouse gases and having a limited impact on the environment [118,119].
Recently, the phenomenon of WtE generation has emerged and gained increasing traction [120,121,122]. In developed countries, it is being successfully implemented as a measure of waste management and energy security. Therefore, many countries have started using waste to recover energy [123]. A WtE system contributes to a sustainable and circular economy in the following ways:
  • Recovering energy from waste can be significantly beneficial in facilitating energy transition and reaching zero-carbon decarbonization targets;
  • WtE methods are instrumental to enhance energy security, reduce reliance on fossil fuels, and generate clean and reliable sources of thermal energy, electricity, and fuels;
  • Implementing a sustainable framework with no contradiction with existing decarbonization measures;
  • One of the most effective approaches to enhance the efficiency of power generation and energy consumption through waste incineration operations;
  • Recovery of secondary raw materials from incineration residues;
  • Delivering a hygienic service to society through municipal waste management and the treatment of combustible non-recyclable waste.
Let us examine how waste to energy is currently applied worldwide. Figure 5 shows the generating capacity of power plants that use renewable energy sources to produce electricity. As presented in Figure 5, the amount of electricity generated by waste globally increased from 2012 to 2021, with Europe, Asia, and North America generating the most electricity from biogas, bioenergy, renewable municipal waste, and solid biofuels.
Despite the growing application of renewable energy and waste in electricity generation in the last decade, fossil fuel is still the primary source of energy. Figure 6 illustrates the level of different types of fuels employed to generate electricity. It is evident that there is a significant difference between renewable energy (including waste energy) and high-carbon fuels. In 2021, nuclear power and renewable energy generated more than one-third (36.7%) of global electricity. As for waste energy, it contributed only 3%, which is a very small percentage. Therefore, countries should pay significant attention to waste resources to generate electricity in order to repurpose waste in a positive way and also diminish coal-fired generator emissions.

4. Result and Discussion

4.1. Drivers and Barriers

This study examines opportunities and barriers to implementing a CE to develop research agendas. Following a review of the literature, several factors have contributed to or prevented a CE, ranging from arguably the “hardest” (technical, economic) to the “softest” (social, institutional) factors. The “drivers/opportunities” are aspects that stimulate and facilitate transitions towards the CE system, while “barriers/obstacles” hinder progress.

4.1.1. General Circular Economy Drivers

The first step to examining the drivers of CE implementation is to identify and understand the motivational factors. Table 2 illustrates these drivers. We have categorized these drivers based on their similarities and definition. Motivational factors and drivers are based on a review of previous literature, including studies undertaken by Pitt and Heinemeyer [125], Ghisellini et al. [113], Lieder and Rashid [117], Govindan and Hasanagic [6], Prieto-Sandoval et al. [126], Cramer [127], Ranta et al. [128], De Jesus and Mendonça [129], Tura et al. [130], Salim et al. [131], Agyemang et al. [132], Gusmerotti et al. [133], Jabbour et al. [134], Dijkstra et al. [135], Jia et al. [136], Aloini et al. [137], Neves and Marques [138], and Neligan et al. [139].

4.1.2. Circular Economy Drivers in Energy Sector

The purpose of this section is to present potential drivers of the circular pathway in the energy sector, which are presented below [140,141,142,143,144,145]:
  • Sustainable energy production—WtE systems that convert waste materials into energy contribute to the transition to a circular economy. In addition to producing a sustainable energy market, these technologies can reduce environmental and health risks associated with waste;
  • Conservation of critical materials—the energy transition will require a shift towards renewable energies by shifting away from fossil fuels towards wind, hydro, solar, and geothermal power or zero-emission technologies supported by batteries. However, the transition to green technologies will lead to a massive demand for minerals like lithium, cobalt, and rare minerals. As IEA [146] reported, achieving the net-zero target by 2040 will require a six-fold increase in mineral input. There could be requirements of more than a 40-fold increase for some critical metals, such as lithium, and over 20-fold for nickel and cobalt. Extraction and mining are the only ways to obtain these materials, which are hazardous to the environment and human health. Moreover, these metals are discovered in relatively small concentrations that are tough to extract, resulting in a more expensive and time-consuming extraction process than other minerals. Through the transition to a CE, economies are capable of recycling these materials from millions of tons of electronic devices like laptops, hard drives, batteries, and other devices. Therefore, it allows countries to eliminate their dependence on mining metals and extend existing materials’ lifespan using circular pathways;
  • Economic development—the combination of circular systems and energy production can lead to economic and ecological improvements. In the production of metals, energy, foods, and other types of products, circular production reduces emissions and energy requirements. By doing so, money can be saved, emissions reduced, and energy production and consumption are decreased. Thus, economies will be less dependent on critical materials because they will be able to recycle them. As a result, a circular and efficient energy market can contribute to economic growth;
  • Environmental drivers—greenhouse gas emissions can be reduced through the use of new technologies and the efficient use of waste materials, such as biogas and biomass;
  • The efficient use of materials—circular economies and recycling technologies allow countries to recycle and reuse 95% of the critical materials, such as aluminium, steel, glass, copper, etc. Therefore, all metals used in batteries (i.e., lithium, nickel, and cobalt) can be recycled. The result is an increase in battery production and a decrease in coal-fired generation units;
  • Waste reduction—the waste disposal process includes five steps: waste transfer, landfill, incineration, waste compaction, and composting. It is both highly harmful to the environment and health and extremely expensive. By using waste resources for energy generation, economies can reduce waste disposal costs and generate electricity, which is vital for human life;
  • Reduction of fossil fuel consumption—WtE facilities instead of coal-fired plants can save over 200,000 barrels of coal per year;
  • Material efficiency—material efficiency developments could offer a valuable alternative solution to current decarbonization policies along with renewable energy use and energy efficiency. By incorporating CE systems into material production, energy consumption can be reduced, thereby reducing greenhouse gas emissions (GHG);
  • Battery recycling—for developing technologies and business models, recycling different types of batteries is placed at the top of the pyramid, and extensive research and development is being conducted, leading to a revolution in circular economies.

4.1.3. General Circular Economy Barriers

Implementing a CE would require fundamental changes in industrial practices and consumption patterns, especially in heavy industries and resource production areas, leading to significant obstacles. In recent years, several publications have developed around barriers that have restricted CE implementation. In order to implement a CE system, we must overcome a number of obstacles that can be classified into the following segments: economic and financial obstacles; knowledge barriers; political challenges; technical roadblocks; cultural obstacles; and regulatory barriers. In this section, we provide a general overview of potential barriers to CE adoption in global economies as well as energy markets, which are presented in Table 3. They are based on studies undertaken by Govindan and Hasanagic [6]; Bet et al., 2018 [7]; Grafström and Aasma [102]; Ranta et al. [128]; de Jesus and Mendonça [129]; Cramer [127]; Salim et al. [131]; Agyemang et al. [132]; Geng et al. [147]; Xue et al. [148]; Zhu and Geng, 2013 [149]; Vanner et al. [150]; Bicket et al. [151]; Gumley [152]; Rizos et al. [153]; Rizos et al. [154]; Böttcher and Müller [155]; Ilić and Nikolić [156]; Pheifer, 2017 [157]; Mont et al. [158]; Wildschut [159]; Hart et al. [160] and Jabbour et al. [161].

4.1.4. Barriers to the CE Acceptance in Energy Industries

The CE strategies are evidently of great importance in the energy market and can have a significant impact on energy transition and decarbonization. While CE creates a variety of benefits and opportunities for the energy market, CE implementation is hampered by a number of practical obstacles that prevent entrepreneurs and policymakers from taking advantage of them. A number of these barriers are outlined below:
  • Government regulations—the current economic policies and regulations are predominantly based on linear economic models, not circular pathways, in energy markets. As a result, there is less governmental support for the CE adoption in the energy sector;
  • Consumer behavior—the level of energy embodied in products is significantly impacted by decisions made by consumers in all types of situations (individuals, industries, and governments) and is capable of reducing energy demand. Accordingly, decisions made by consumers play an important role in the development of circular economies. However, a reverse condition exists, and consumer attitudes and demands are major barriers to the CE implementation. Energy efficiency, environmental protection, recycling, and circular systems are not well known by the general public [162,163];
  • Energy transition—in today’s world, climate change, global warming, and health problems caused by greenhouse gases are the major issues. As a result, political attention has shifted to the green energy transition nationally and internationally. Accordingly, the political, governmental, and energy authorities focus mainly on the green energy transition. There is a struggle among governments to involve the public and businesses in this transition. Therefore, the circular transition receives less attention from the government and entrepreneurs in energy markets;
  • Emphasis on renewable energy—energy transition refers to the transition from traditional fossil-fuel-based energy production and consumption systems to renewable energy sources. As a result, the primary focus of research is to develop renewable systems, energy sustainable technologies, and renewable generations. Consequently, there is a lack of knowledge and awareness about circular systems in energy markets;
  • Lack of battery recycling technologies—developing long-life batteries plays a crucial role, specifically in the energy and transportation sectors. A wide range of batteries are designed for energy storage systems and electric vehicles. Lithium-ion batteries are likely to play a major role as they are widely used in electronic devices (i.e., mobile phones, laptops, digital cameras) and electric vehicles (EVs). However, the energy sector faces a new challenge with the development of batteries, which is battery recycling;
  • Batteries consist of hazardous materials that can be classified as hazardous waste [164]. Most batteries are composed of toxic materials such as lead, cadmium, mercury, nickel, or copper, which are all hazardous to human health and the environment and pose a threat to water sources and ecosystems if they leach out of landfills [165,166]. However, most batteries are not properly recycled, especially lithium-ion batteries, which are expensive and difficult to recycle. The number of lithium-ion batteries being recycled is still relatively low due to the cost of recycling and the immaturity of recycling processes. These batteries have been designed and manufactured in ways that make it difficult to repair, remanufacture, or recycle them. As a result, two key issues arise here: (1) lack of recycling technologies in battery industries; (2) as material markets fluctuate, it can be difficult to achieve economic efficiency in battery recycling;
  • Lack of recycling infrastructure for wind energy markets—millions of tons of composite materials have recently been used in the world wind energy sector and construction of wind turbine blades such as glass fiber, composite materials, fiber, resin, wood, foam, adhesives, coatings, copper, and steel. The recycling infrastructure for turbine blade materials is still under development, requiring further research and implementation. For such materials, recycling infrastructures have not yet been established, studies about end-of-life treatment technologies remain in the developmental stage, and there are no secondary markets for recycled materials [167];
  • In light of the global transition towards sustainable and green environments, biofuels would be a good step toward a cleaner pathway. Compared with petroleum-based fuels, biofuels come from renewable resources and often produce cleaner emissions than fossil fuels. However, water, land, forests, and fertilizers required for sufficient biofuel production may result in other issues, such as food crisis, water depletion, contamination of lands, deforestation, fertilizer-related pollutants, and other environmental risks [168,169].

4.2. Recommendations and Solutions

By considering the economic and political aspects of CE implementation, various approaches can be taken to address the challenges and promote the solutions outlined in Table 4.
To address the lack of framework discussed previously in the barrier section, economic strategies, CE perspectives, and decarbonization policies must be evaluated simultaneously in order to establish a clean energy-based economy that targets economic growth. The recommendations and mentioned policies are imperative solutions for CE adoption and can create a sustainable and essential framework for economies and industries to move from a linear to a circular system.

5. Conclusions

Sustainability is a strategic approach to develop a more sustainable global economy to support the environment and socioeconomic development. Literature on sustainability has been concerned mainly on global warming and environmental degradation issues, whereas a CE concept has recently been suggested as an alternative solution to support market sustainability and deal with both environmental and socioeconomic challenges. To tackle these challenges, countries must switch from linear economies that follow the “take-make-dispose” principle to circular and sustainable economies. The CE approach focuses on the transformation of waste into resources and linking production with consumption activities. In spite of the CE importance in all economies, this area of research has received little attention. The aim of this study is to uncover the most important determinants of circular strategies from a global economic perspective through a structural and conceptual literature review. The study examines barriers to the CE adoption and proposes drivers and measures to overcome them.
In terms of energy, recent years have seen an acceleration of ambitions regarding energy transition and decarbonization, particularly in terms of achieving net-zero carbon emission targets. For net-zero targets and energy efficient development, all sectors, primarily the energy industry, will need to modify their infrastructures, a process that will require extensive reconstruction and retrofitting at high costs. Furthermore, the linear decarbonization process focuses only on reducing emissions from energy production and renewable energy consumption, which are not sufficient to achieve net-zero emissions. Recently, the CE approach has been gaining attention as a means to accelerate decarbonization and facilitate energy efficiency. Therefore, CE approaches are complementary to existing energy and decarbonization policies in promoting energy transitions toward a cleaner environment. Circularity emphasizes the transformation of waste into resources. Nowadays, recycling materials and waste in an efficient manner are imperative to maintain a sustainable environment. Accordingly, this paper aims to analyze various aspects related to implementing the CE approaches at the macro and energy levels.
A systematic literature review indicates that circularity is an essential strategy to attain sustainable development. The CE structure should be considered a sustainable framework to enhance economic growth by reducing waste, protecting natural resources, managing resource scarcity, recycling materials, improving energy efficiency, and recirculating them into the economy. Findings reveal that the circular system is a key pillar of sustainability, security, and efficiency in the energy sector.
In terms of the energy concept, the study concluded that the integration of CE approaches in economies through coherent public policy approaches must be considered as an essential component of existing decarbonization instruments, since they are capable of both increasing efficiency and decarbonizing during the energy transition. Embedding the CE principles into the design process is essential for the sustainable energy transition. It also found that both the public and private sectors need to move away from linear paradigms to achieve CE implementation. From a technological perspective, countries have the potential to produce electricity from biomass, biogas, wind, and solar, or use energy store systems or portable batteries. As traditional technologies and coal-fired power stations are replaced by infrastructures and new technologies, it is essential to apply CE principles to unlock waste’s resource potential and minimize its management challenges. As an example, WtE generation technologies contribute to a sustainable and circular economy in various ways. These technologies utilize waste to generate energy in the form of electricity or heat. A WtE system contributes to a sustainable and circular economy in various ways.
It has been discovered that there are major barriers that need to be overcome in order to create a circular economy that is capable of bringing socio-economic and environmental benefits to the wider economy. There are practical barriers to the CE adoption in economies, including economic and financial obstacles, regulatory policies that are dominantly targeted towards traditional and linear economic models and hence linear decarbonization policies, knowledge barriers, cultural obstacles, and technical limitations. It is interesting to note that obstacles are interconnected. For example, the lack of CE policies reflects a lack of awareness and knowledge about the CE concept among the regulatory authorities. On the other hand, the levels of knowledge and awareness of consumers are reflected in regulators’ knowledge levels. It indicates that all aspects of society can contribute to adopting and implementing circular economic systems. Therefore, the first step in the transition from a linear to a circular economy is enhancing social knowledge of the CE necessity. In addition, economic strategies, CE perspectives, and decarbonization policies must be evaluated simultaneously in order to address obstacles and implement a clear public policy framework.
According to the findings, circularity is frequently the subject of research among scientists and professionals. However, the CE development requires the involvement of governmental bodies, policymakers, and stakeholders beyond the expert community to surge knowledge of the necessity of CE and its accomplishment. Circularity can be considered as a novel and innovative approach in alleviating the contradiction between the rapid economic growth and shortages of energy and raw materials. This paper will stimulate and motivate governmental bodies to invest in circular developments and bio-energy generators to reduce emissions. Moreover, since eco-circular approaches are developed to enhance efficient resource allocation, CE approaches should remain applicable even once zero-emission targets are achieved.

Funding

This research received no external funding.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Cherp, A.; Jewell, J.; Vinichenko, V.; Bauer, N.; De Cian, E. Global energy security under different climate policies, GDP growth rates and fossil resource availabilities. Clim. Chang. 2013, 136, 83–94. [Google Scholar] [CrossRef]
  2. Wang, Q.; Zhou, K. A framework for evaluating global national energy security. Appl. Energy 2017, 188, 19–31. [Google Scholar] [CrossRef]
  3. Qin, L.; Wang, M.; Zhu, J.; Wei, Y.; Zhou, X.; He, Z. Towards Circular Economy through Waste to Biomass Energy in Madagascar. Complexity 2021, 2021, 5822568. [Google Scholar] [CrossRef]
  4. Steffen, W.; Richardson, K.; Rockström, J.; Cornell, S.E.; Fetzer, I.; Bennett, E.M.; Biggs, R.; Carpenter, S.R.; De Vries, W.; De Wit, C.A.; et al. Planetary boundaries: Guiding human development on a changing planet. Science 2015, 347, 1259855. [Google Scholar] [CrossRef]
  5. Franklin-Johnson, E.; Figge, F.; Canning, L. Resource duration as a managerial indicator for Circular Economy performance. J. Clean. Prod. 2016, 133, 589–598. [Google Scholar] [CrossRef]
  6. Govindan, K.; Hasanagic, M. A systematic review on drivers, barriers, and practices towards circular economy: A supply chain perspective. Int. J. Prod. Res. 2017, 56, 278–311. [Google Scholar] [CrossRef]
  7. Bet, B.; Kas, J.; Truijens, D.; Lee, S.V.D.; Broere, J.; Leising, E.; Nuninga, T.; Bose, P.; Ravensberg, E.V.; Francesco, E.D.; et al. Barriers and Best Practices for the Circular Economy. 2018. Available online: https://core.ac.uk/download/pdf/154412546.pdf (accessed on 30 December 2018).
  8. World Nuclear Association. Carbon Dioxide Emissions from Electricity. 2022. Available online: https://www.world-nuclear.org/ (accessed on 20 September 2020).
  9. IEA Online Data Services. Global Energy Review: CO2 Emissions in 2021. Available online: https://www.iea.org/reports/global-energy-review-co2-emissions-in-2021-2 (accessed on 28 July 2022).
  10. European Environmental Agency. Emerging Waste Streams: Opportunities and Challenges of the Clean-Energy Transition from a Circular Economy Perspective. 2021. Available online: https://www.eea.europa.eu/publications/emerging-waste-streams-opportunities-and (accessed on 24 August 2021).
  11. MacArthur, E. Founding Partners of the towards the Circular Economy Economic and Business Rationale for an Accelerated Transition. 2012. Available online: https://www.aquafil.com/assets/uploads/ellen-macarthur-foundation.pdf (accessed on 30 September 2012).
  12. Jawahir, I.; Bradley, R. Technological Elements of Circular Economy and the Principles of 6R-Based Closed-loop Material Flow in Sustainable Manufacturing. Procedia CIRP 2016, 40, 103–108. [Google Scholar] [CrossRef]
  13. Ghisellini, P.; Cialani, C.; Ulgiati, S. A Review on Circular Economy: The Expected Transition to a Balanced Interplay of Environmental and Economic Systems. J. Clean. Prod. 2016, 114, 11–32. [Google Scholar] [CrossRef]
  14. Ozili, P.K. Circular Economy, Banks, and Other Financial Institutions: What’s in It for Them? Circ. Econ. Sustain. 2021, 1, 787–798. [Google Scholar] [CrossRef]
  15. Barros, M.V.; Salvador, R.; Prado, G.F.D.; de Francisco, A.C.; Piekarski, C.M. Circular economy as a driver to sustainable businesses. Clean. Environ. Syst. 2020, 2, 100006. [Google Scholar] [CrossRef]
  16. Unleashing the Power of the Bio-Economy. Ind. Biotechnol. 2013, 9, 74–80. [CrossRef]
  17. Bag, S.; Sahu, A.K.; Kilbourn, P.; Pisa, N.; Dhamija, P.; Sahu, A.K. Modeling barriers of digital manufacturing in a circular economy for enhancing sustainability. Int. J. Prod. Perform. Manag. 2021, 71, 833–869. [Google Scholar] [CrossRef]
  18. Ponis, S.; Aretoulaki, E.; Maroutas, T.; Plakas, G.; Dimogiorgi, K. A Systematic Literature Review on Additive Manufacturing in the Context of Circular Economy. Sustainability 2021, 13, 6007. [Google Scholar] [CrossRef]
  19. Velasco-Muñoz, J.F.; Aznar-Sánchez, J.A.; López-Felices, B.; Román-Sánchez, I.M. Circular economy in agriculture. An analysis of the state of research based on the life cycle. Sustain. Prod. Consum. 2022, 34, 257–270. [Google Scholar] [CrossRef]
  20. Altamira-Algarra, B.; Puigagut, J.; Day, J.W.; Mitsch, W.J.; Vymazal, J.; Hunter, R.G.; García, J. A review of technologies for closing the P loop in agriculture runoff: Contributing to the transition towards a circular economy. Ecol. Eng. 2022, 177, 106571. [Google Scholar] [CrossRef]
  21. Hazen, B.T.; Russo, I.; Confente, I.; Pellathy, D. Supply chain management for circular economy: Conceptual framework and research agenda. Int. J. Logist. Manag. 2020, 32, 510–537. [Google Scholar] [CrossRef]
  22. Calzolari, T.; Genovese, A.; Brint, A. Circular Economy indicators for supply chains: A systematic literature review. Environ. Sustain. Indic. 2021, 13, 100160. [Google Scholar] [CrossRef]
  23. Fernando, Y.; Tseng, M.-L.; Aziz, N.; Ikhsan, R.B.; Wahyuni-Td, I.S. Waste-to-energy supply chain management on circular economy capability: An empirical study. Sustain. Prod. Consum. 2022, 31, 26–38. [Google Scholar] [CrossRef]
  24. Reynolds, J.; Kennedy, R.; Ichapka, M.; Agarwal, A.; Oke, A.; Cox, E.; Edwards, C.; Njuguna, J. An evaluation of feedstocks for sustainable energy and circular economy practices in a small island community. Renew. Sustain. Energy Rev. 2022, 161, 112360. [Google Scholar] [CrossRef]
  25. Abdelmeguid, A.; Afy-Shararah, M.; Salonitis, K. Investigating the challenges of applying the principles of the circular economy in the fashion industry: A systematic review. Sustain. Prod. Consum. 2022, 32, 505–518. [Google Scholar] [CrossRef]
  26. Moorhouse, D. Circular economy in fashion and textiles. Int. J. Sustain. Fash. Text. 2022, 1, 169–173. [Google Scholar] [CrossRef]
  27. Nguyen, M.D.; Thomas, M.; Surapaneni, A.; Moon, E.M.; Milne, N.A. Beneficial reuse of water treatment sludge in the context of circular economy. Environ. Technol. Innov. 2022, 28, 102651. [Google Scholar] [CrossRef]
  28. Mannina, G.; Gulhan, H.; Ni, B.-J. Water reuse from wastewater treatment: The transition towards circular economy in the water sector. Bioresour. Technol. 2022, 363, 127951. [Google Scholar] [CrossRef]
  29. Linnenluecke, M.K.; Griffiths, A. Firms and sustainability: Mapping the intellectual origins and structure of the corporate sustainability field. Glob. Environ. Chang. 2012, 23, 382–391. [Google Scholar] [CrossRef]
  30. De Angelis, R.; Howard, M.; Miemczyk, J. Supply chain management and the circular economy: Towards the circular supply chain. Prod. Plan. Control. 2018, 29, 425–437. [Google Scholar] [CrossRef]
  31. Farooque, M.; Zhang, A.; Liu, Y. Barriers to circular food supply chains in China. Supply Chain Manag. Int. J. 2019, 24, 677–696. [Google Scholar] [CrossRef]
  32. Hussain, M.; Malik, M. Organizational enablers for circular economy in the context of sustainable supply chain management. J. Clean. Prod. 2020, 256, 120375. [Google Scholar] [CrossRef]
  33. Kumar, P.; Singh, R.K.; Kumar, V. Managing supply chains for sustainable operations in the era of industry 4.0 and circular economy: Analysis of barriers. Resour. Conserv. Recycl. 2020, 164, 105215. [Google Scholar] [CrossRef]
  34. Toop, T.A.; Ward, S.; Oldfield, T.; Hull, M.; Kirby, M.E.; Theodorou, M.K. AgroCycle–Developing a circular economy in agriculture. Energy Procedia 2017, 123, 76–80. [Google Scholar] [CrossRef]
  35. Esposito, B.; Sessa, M.R.; Sica, D.; Malandrino, O. Towards Circular Economy in the Agri-Food Sector. A Systematic Literature Review. Sustainability 2020, 12, 7401. [Google Scholar] [CrossRef]
  36. Gkountani, V.A.; Tsoulfas, G.T.; Rachaniotis, N.P. Circular economy and resilience: Convergences and deviations in the case of agri-food supply chains. IOP Conf. Ser. Earth Environ. Sci. 2021, 899, 012001. [Google Scholar] [CrossRef]
  37. Liu, Y.; Wood, L.C.; Venkatesh, V.; Zhang, A.; Farooque, M. Barriers to sustainable food consumption and production in China: A fuzzy DEMATEL analysis from a circular economy perspective. Sustain. Prod. Consum. 2021, 28, 1114–1129. [Google Scholar] [CrossRef]
  38. van Leeuwen, K.; de Vries, E.; Koop, S.; Roest, K. The Energy & Raw Materials Factory: Role and Potential Contribution to the Circular Economy of the Netherlands. Environ. Manag. 2018, 61, 786–795. [Google Scholar] [CrossRef]
  39. Priyadarshini, P.; Abhilash, P.C. Circular economy practices within energy and waste management sectors of India: A meta-analysis. Bioresour. Technol. 2020, 304, 123018. [Google Scholar] [CrossRef] [PubMed]
  40. Holmberg, T.; Ideland, M. The circular economy of food waste: Transforming waste to energy through ‘make-up’ work. J. Mater. Cult. 2021, 26, 344–361. [Google Scholar] [CrossRef]
  41. Hugo, A.d.A.; de Nadae, J.; Lima, R.D.S. Can Fashion Be Circular? A Literature Review on Circular Economy Barriers, Drivers, and Practices in the Fashion Industry’s Productive Chain. Sustainability 2021, 13, 12246. [Google Scholar] [CrossRef]
  42. Radhakrishnan, S. Circular Economy in Textiles and Fashion. In Circular Economy; Springer: Singapore, 2021; pp. 163–202. [Google Scholar] [CrossRef]
  43. Chen, X.; Memon, H.A.; Wang, Y.; Marriam, I.; Tebyetekerwa, M. Circular Economy and Sustainability of the Clothing and Textile Industry. Mater. Circ. Econ. 2021, 3, 1–9. [Google Scholar] [CrossRef]
  44. Paletta, A.; Filho, W.L.; Balogun, A.-L.; Foschi, E.; Bonoli, A. Barriers and challenges to plastics valorisation in the context of a circular economy: Case studies from Italy. J. Clean. Prod. 2019, 241, 118149. [Google Scholar] [CrossRef]
  45. Acerbi, F.; Taisch, M. A literature review on circular economy adoption in the manufacturing sector. J. Clean. Prod. 2020, 273, 123086. [Google Scholar] [CrossRef]
  46. Badhotiya, G.K.; Avikal, S.; Soni, G.; Sengar, N. Analyzing barriers for the adoption of circular economy in the manufacturing sector. Int. J. Prod. Perform. Manag. 2021, 71, 912–931. [Google Scholar] [CrossRef]
  47. Susanty, A.; Tjahjono, B.; Sulistyani, R.E. An investigation into circular economy practices in the traditional wooden furniture industry. Prod. Plan. Control. 2020, 31, 1336–1348. [Google Scholar] [CrossRef]
  48. Hartini, S.; Wicaksono, P.A.; Rizal, A.M.D.; Hamdi, M. Integration lean manufacturing and 6R to reduce wood waste in furniture company toward circular economy. IOP Conf. Ser. Mater. Sci. Eng. 2021, 1072, 012067. [Google Scholar] [CrossRef]
  49. Paul, S.; Ali, S.M.; Hasan, M.A.; Paul, S.K.; Kabir, G. Critical Success Factors for Supply Chain Sustainability in the Wood Industry: An Integrated PCA-ISM Model. Sustainability 2022, 14, 1863. [Google Scholar] [CrossRef]
  50. Ayçin, E.; Kaya, S.K. Towards the circular economy: Analysis of barriers to implementation of Turkey’s zero waste management using the fuzzy DEMATEL method. Waste Manag. Res. J. Sustain. Circ. Econ. 2021, 39, 1078–1089. [Google Scholar] [CrossRef]
  51. Liu, Q.; Yang, L.; Yang, M. Digitalisation for Water Sustainability: Barriers to Implementing Circular Economy in Smart Water Management. Sustainability 2021, 13, 11868. [Google Scholar] [CrossRef]
  52. Salminen, J.; Määttä, K.; Haimi, H.; Maidell, M.; Karjalainen, A.; Noro, K.; Koskiaho, J.; Tikkanen, S.; Pohjola, J. Water-smart circular economy–Conceptualisation, transitional policy instruments and stakeholder perception. J. Clean. Prod. 2021, 334, 130065. [Google Scholar] [CrossRef]
  53. Simon, B. What are the most significant aspects of supporting the circular economy in the plastic industry? Resour. Conserv. Recycl. 2018, 141, 299–300. [Google Scholar] [CrossRef]
  54. Guyot Phung, C. Implications of the circular economy and digital transition on skills and green jobs in the plastics industry. Field Actions Science Reports. J. Field Actions 2019, 19, 100–107. [Google Scholar]
  55. Alvarez-Risco, A.; Rosen, M.A.; Del-Aguila-Arcentales, S. A New Regulation for Supporting a Circular Economy in the Plastic Industry: The Case of Peru (Short Communication). J. Landsc. Ecol. 2020, 13, 1–3. [Google Scholar] [CrossRef]
  56. Klein, N.; Ramos, T.B.; Deutz, P. Circular Economy Practices and Strategies in Public Sector Organizations: An Integrative Review. Sustainability 2020, 12, 4181. [Google Scholar] [CrossRef]
  57. Barreiro-Gen, M.; Lozano, R. How circular is the circular economy? Analysing the implementation of circular economy in organisations. Bus. Strat. Environ. 2020, 29, 3484–3494. [Google Scholar] [CrossRef]
  58. Droege, H.; Raggi, A.; Ramos, T.B. Overcoming Current Challenges for Circular Economy Assessment Implementation in Public Sector Organisations. Sustainability 2021, 13, 1182. [Google Scholar] [CrossRef]
  59. Saidani, M.; Yannou, B.; Leroy, Y.; Cluzel, F. Heavy vehicles on the road towards the circular economy: Analysis and comparison with the automotive industry. Resour. Conserv. Recycl. 2018, 135, 108–122. [Google Scholar] [CrossRef]
  60. Kayikci, Y.; Kazancoglu, Y.; Lafci, C.; Gozacan, N. Exploring barriers to smart and sustainable circular economy: The case of an automotive eco-cluster. J. Clean. Prod. 2021, 314, 127920. [Google Scholar] [CrossRef]
  61. Sopha, B.M.; Purnamasari, D.M.; Ma’Mun, S. Barriers and Enablers of Circular Economy Implementation for Electric-Vehicle Batteries: From Systematic Literature Review to Conceptual Framework. Sustainability 2022, 14, 6359. [Google Scholar] [CrossRef]
  62. Baldassarre, B.; Maury, T.; Mathieux, F.; Garbarino, E.; Antonopoulos, I.; Sala, S. Drivers and Barriers to the Circular Economy Transition: The Case of Recycled Plastics in the Automotive Sector in the European Union. Procedia CIRP 2022, 105, 37–42. [Google Scholar] [CrossRef]
  63. Jones, P.; Comfort, D. The construction industry and the circular economy. Int. J. Manag. Cases 2018, 20, 4–15. [Google Scholar]
  64. Bilal, M.; Khan, K.I.A.; Thaheem, M.J.; Nasir, A.R. Current state and barriers to the circular economy in the building sector: Towards a mitigation framework. J. Clean. Prod. 2020, 276, 123250. [Google Scholar] [CrossRef]
  65. Hjaltadóttir, R.E.; Hild, P. Circular Economy in the building industry European policy and local practices. Eur. Plan. Stud. 2021, 29, 2226–2251. [Google Scholar] [CrossRef]
  66. Giorgi, S.; Lavagna, M.; Wang, K.; Osmani, M.; Liu, G.; Campioli, A. Drivers and barriers towards circular economy in the building sector: Stakeholder interviews and analysis of five European countries policies and practices. J. Clean. Prod. 2022, 336, 130395. [Google Scholar] [CrossRef]
  67. Brightley, C. Tourism and the circular economy. IGCAT Int. Inst. Gastron. Cult. Arts Tour. 2017, 12, 4–7. [Google Scholar]
  68. Falcone, P.M. Tourism-Based Circular Economy in Salento (South Italy): A SWOT-ANP Analysis. Soc. Sci. 2019, 8, 216. [Google Scholar] [CrossRef] [Green Version]
  69. Vatansever, K.; Akarsu, H.; Kazançoğlu, Y. Evaluation of Transition Barriers to Circular Economy: A Case from the Tourism Industry. Int. J. Math. Eng. Manag. Sci. 2021, 6, 824–846. [Google Scholar] [CrossRef]
  70. Korhonen, J.; Honkasalo, A.; Seppälä, J. Circular economy: The concept and its limitations. Ecol. Econ. 2018, 143, 37–46. [Google Scholar] [CrossRef]
  71. Kinnunen, P.H.-M.; Kaksonen, A.H. Towards circular economy in mining: Opportunities and bottlenecks for tailings valorization. J. Clean. Prod. 2019, 228, 153–160. [Google Scholar] [CrossRef]
  72. Singh, R.K.; Kumar, A.; Garza-Reyes, J.A.; de Sá, M.M. Managing operations for circular economy in the mining sector: An analysis of barriers intensity. Resour. Policy 2020, 69, 101752. [Google Scholar] [CrossRef]
  73. Gedam, V.V.; Raut, R.D.; Jabbour, A.B.L.D.S.; Agrawal, N. Moving the circular economy forward in the mining industry: Challenges to closed-loop in an emerging economy. Resour. Policy 2021, 74, 102279. [Google Scholar] [CrossRef]
  74. Luthra, S.; Mangla, S.K.; Sarkis, J.; Tseng, M.-L. Resources melioration and the circular economy: Sustainability potentials for mineral, mining and extraction sector in emerging economies. Resour. Policy 2022, 77, 102652. [Google Scholar] [CrossRef]
  75. Gama, M.; Herrmann, C.; Fisher, T. Circular economy in the electronics sector: A holistic perspective. In Proceedings of the 2016 Electronics Goes Green 2016+(EGG), Berlin, Germany, 1–3 September 2016; pp. 1–7. [Google Scholar] [CrossRef]
  76. O’Connor, M.P.; Zimmerman, J.B.; Anastas, P.T.; Plata, D.L. A Strategy for Material Supply Chain Sustainability: Enabling a Circular Economy in the Electronics Industry through Green Engineering. ACS Sustain. Chem. Eng. 2016, 4, 5879–5888. [Google Scholar] [CrossRef]
  77. Curtis, T.L.; Buchanan, H.; Smith, L.; Heath, G. A Circular Economy for Solar Photovoltaic System Materials: Drivers, Barriers, Enablers, and U.S. Policy Considerations; (No. NREL/TP-6A20-74550); National Renewable Energy Lab. (NREL): Golden, CO, USA, 2021. [Google Scholar] [CrossRef]
  78. Rizos, V.; Bryhn, J. Implementation of circular economy approaches in the electrical and electronic equipment (EEE) sector: Barriers, enablers and policy insights. J. Clean. Prod. 2022, 338, 130617. [Google Scholar] [CrossRef]
  79. van Keulen, M.; Kirchherr, J. The implementation of the Circular Economy: Barriers and enablers in the coffee value chain. J. Clean. Prod. 2020, 281, 125033. [Google Scholar] [CrossRef]
  80. Pires, A.M.A. A Circular Economy Approach to the Coffee Industrys Waste: The Case of Delta Cafés. Master’s Thesis, Nova School of Business and Economics (NSBE), Carcavelos, Portugal, 2022. [Google Scholar]
  81. Moktadir, A.; Ahmadi, H.B.; Sultana, R.; Zohra, F.-T.; Liou, J.J.; Rezaei, J. Circular economy practices in the leather industry: A practical step towards sustainable development. J. Clean. Prod. 2019, 251, 119737. [Google Scholar] [CrossRef]
  82. Karuppiah, K.; Sankaranarayanan, B.; Ali, S.M.; Jabbour, C.J.C.; Bhalaji, R. Inhibitors to circular economy practices in the leather industry using an integrated approach: Implications for sustainable development goals in emerging economies. Sustain. Prod. Consum. 2021, 27, 1554–1568. [Google Scholar] [CrossRef]
  83. Cabrera-Codony, A.; Ruiz, B.; Gil, R.; Popartan, L.A.; Santos-Clotas, E.; Martín, M.J.; Fuente, E. From biocollagenic waste to efficient biogas purification: Applying circular economy in the leather industry. Environ. Technol. Innov. 2020, 21, 101229. [Google Scholar] [CrossRef]
  84. Van Buren, N.; Demmers, M.; Van Der Heijden, R.; Witlox, F. Towards a Circular Economy: The Role of Dutch Logistics Industries and Governments. Sustainability 2016, 8, 647. [Google Scholar] [CrossRef]
  85. Dutta, P.; Talaulikar, S.; Xavier, V.; Kapoor, S. Fostering reverse logistics in India by prominent barrier identification and strategy implementation to promote circular economy. J. Clean. Prod. 2021, 294, 126241. [Google Scholar] [CrossRef]
  86. Gupta, A.; Singh, R.K. Applications of emerging technologies in logistics sector for achieving circular economy goals during COVID-19 pandemic: Analysis of critical success factors. Int. J. Logist. Res. Appl. 2021, 1–22. [Google Scholar] [CrossRef]
  87. Saraç, M.; Hassan, M.; Alam, A. Circular Economy, Sustainable Development, and the Role of Islamic Finance. Islamic Perspective for Sustainable Financial System; Istanbul University Press: Istanbul, Turkey, 2020; pp. 1–26. [Google Scholar] [CrossRef]
  88. Gonçalves, B.d.S.M.; de Carvalho, F.L.; Fiorini, P.D.C. Circular Economy and Financial Aspects: A Systematic Review of the Literature. Sustainability 2022, 14, 3023. [Google Scholar] [CrossRef]
  89. MacNeill, A.J.; Hopf, H.; Khanuja, A.; Alizamir, S.; Bilec, M.; Eckelman, M.J.; Hernandez, L.; McGain, F.; Simonsen, K.; Thiel, C.; et al. Transforming the Medical Device Industry: Road Map to A Circular Economy. Health Aff. 2020, 39, 2088–2097. [Google Scholar] [CrossRef]
  90. Kandasamy, J.; Kinare, Y.P.; Pawar, M.T.; Majumdar, A.; K.E.K., V.; Agrawal, R. Circular economy adoption challenges in medical waste management for sustainable development: An empirical study. Sustain. Dev. 2022, 30, 958–975. [Google Scholar] [CrossRef]
  91. Laso, J.; García-Herrero, I.; Margallo, M.; Vázquez-Rowe, I.; Fullana, P.; Bala, A.; Gazulla, C.; Irabien, A.; Aldaco, R. Finding an economic and environmental balance in value chains based on circular economy thinking: An eco-efficiency methodology applied to the fish canning industry. Resour. Conserv. Recycl. 2018, 133, 428–437. [Google Scholar] [CrossRef]
  92. Milios, L.; Beqiri, B.; Whalen, K.A.; Jelonek, S.H. Sailing towards a circular economy: Conditions for increased reuse and remanufacturing in the Scandinavian maritime sector. J. Clean. Prod. 2019, 225, 227–235. [Google Scholar] [CrossRef]
  93. Okumus, D.; Gunbeyaz, S.A.; Kurt, R.E.; Turan, O. Towards a circular maritime industry: Identifying strategy and technology solutions. J. Clean. Prod. 2023, 382, 134935. [Google Scholar] [CrossRef]
  94. Stavileci, S.; Andersson, D. An Assessment of How Circular Economy Can Be Implemented in the Aerospace Industry. 2015. Available online: http://www.diva-portal.org/smash/get/diva2:839020/FULLTEXT02.pdf (accessed on 30 December 2015).
  95. Brennan, L.; Vecchi, A. The orbital circular economy framework: Emblematic evidence from the space industry. Kindai Manag. Rev. 2020, 8, 81–92. [Google Scholar]
  96. Dias, V.M.R.; Jugend, D.; Fiorini, P.D.C.; Razzino, C.D.A.; Pinheiro, M.A.P. Possibilities for applying the circular economy in the aerospace industry: Practices, opportunities and challenges. J. Air Transp. Manag. 2022, 102, 102227. [Google Scholar] [CrossRef]
  97. Fortunati, S.; Martiniello, L.; Morea, D. The Strategic Role of the Corporate Social Responsibility and Circular Economy in the Cosmetic Industry. Sustainability 2020, 12, 5120. [Google Scholar] [CrossRef]
  98. Lourenço-Lopes, C.; Fraga-Corral, M.; Jimenez-Lopez, C.; Pereira, A.; Garcia-Oliveira, P.; Carpena, M.; Prieto, M.; Simal-Gandara, J. Metabolites from Macroalgae and Its Applications in the Cosmetic Industry: A Circular Economy Approach. Resources 2020, 9, 101. [Google Scholar] [CrossRef]
  99. Morea, D.; Fortunati, S.; Martiniello, L. Circular economy and corporate social responsibility: Towards an integrated strategic approach in the multinational cosmetics industry. J. Clean. Prod. 2021, 315, 128232. [Google Scholar] [CrossRef]
  100. Boulding, K.E. The Economics of the Coming Spaceship Earth; Resources for the Future: Washington DC, USA, 1966; pp. 1–17. [Google Scholar]
  101. Segerson, K.; Pearce, D.W.; Turner, R.K. Economics of Natural Resources and the Environment. Land Econ. 1989, 67, 272. [Google Scholar] [CrossRef]
  102. Grafström, J.; Aasma, S. Breaking circular economy barriers. J. Clean. Prod. 2021, 292, 126002. [Google Scholar] [CrossRef]
  103. Andersen, M.S. An introductory note on the environmental economics of the circular economy. Sustain. Sci. 2006, 2, 133–140. [Google Scholar] [CrossRef]
  104. Su, B.; Heshmati, A.; Geng, Y.; Yu, X. A review of the circular economy in China: Moving from rhetoric to implementation. J. Clean. Prod. 2013, 42, 215–227. [Google Scholar] [CrossRef]
  105. Geissdoerfer, M.; Savaget, P.; Bocken, N.M.P.; Hultink, E.J. The circular economy—A new sustainability paradigm? J. Clean. Prod. 2017, 143, 757–768. [Google Scholar] [CrossRef]
  106. Stahel, W.; Reday, G. The Potential for Substituting Manpower for Energy, Report to the Commission of the European Communities. 1976. Available online: https://www.econbiz.de/Record/the-potential-for-substituting-manpower-for-energy-final-report-30-july-1977-for-the-commission-of-the-european-communities-reday-mulvey-genevi%C3%A8ve/10000552301 (accessed on 30 July 1977).
  107. Christis, M.; Athanassiadis, A.; Vercalsteren, A. Implementation at a city level of circular economy strategies and climate change mitigation–The case of Brussels. J. Clean. Prod. 2019, 218, 511–520. [Google Scholar] [CrossRef]
  108. Sassanelli, C.; Rosa, P.; Rocca, R.; Terzi, S. Circular economy performance assessment methods: A systematic literature review. J. Clean. Prod. 2019, 229, 440–453. [Google Scholar] [CrossRef]
  109. Kristensen, H.S.; Mosgaard, M.A. A review of micro level indicators for a circular economy–Moving away from the three dimensions of sustainability? J. Clean. Prod. 2020, 243, 118531. [Google Scholar] [CrossRef]
  110. De Pascale, A.; Arbolino, R.; Szopik-Depczyńska, K.; Limosani, M.; Ioppolo, G. A systematic review for measuring circular economy: The 61 indicators. J. Clean. Prod. 2021, 281, 124942. [Google Scholar] [CrossRef]
  111. Mhatre, P.; Panchal, R.; Singh, A.; Bibyan, S. A systematic literature review on the circular economy initiatives in the European Union. Sustain. Prod. Consum. 2021, 26, 187–202. [Google Scholar] [CrossRef]
  112. Cayzer, S.; Griffiths, P.; Beghetto, V. Design of indicators for measuring product performance in the circular economy. Int. J. Sustain. Eng. 2017, 10, 289–298. [Google Scholar] [CrossRef]
  113. Jackson, M.; Lederwasch, A.; Giurco, D. Transitions in Theory and Practice: Managing Metals in the Circular Economy. Resources 2014, 3, 516–543. [Google Scholar] [CrossRef] [Green Version]
  114. Wilts, H. The Circular Economy; Kick-Starting the Transformation, The Friedrich Ebert Stiftung, Economic and Social policies. 2019. Available online: https://library.fes.de/pdf-files/wiso/19034.pdf (accessed on 28 February 2019).
  115. METI. Handbook on Resource Recycling Legislation and 3R Initiatives; Ministry of Economy, Trade and Industry: Tokyo, Japan, 2004. [Google Scholar]
  116. Morioka, T.; Tsunemi, K.; Yamamoto, Y.; Yabar, H.; Yoshida, N. Eco-efficiency of Advanced Loop-closing Systems for Vehicles and Household Appliances in Hyogo Eco-town. J. Ind. Ecol. 2005, 9, 205–221. [Google Scholar] [CrossRef]
  117. Lieder, M.; Rashid, A. Towards circular economy implementation: A comprehensive review in context of manufacturing industry. J. Clean. Prod. 2016, 115, 36–51. [Google Scholar] [CrossRef]
  118. Makarichi, L.; Jutidamrongphan, W.; Techato, K.-A. The evolution of waste-to-energy incineration: A review. Renew. Sustain. Energy Rev. 2018, 91, 812–821. [Google Scholar] [CrossRef]
  119. Khalil, M.; Berawi, M.A.; Heryanto, R.; Rizalie, A. Waste to energy technology: The potential of sustainable biogas production from animal waste in Indonesia. Renew. Sustain. Energy Rev. 2019, 105, 323–331. [Google Scholar] [CrossRef]
  120. Themelis, N.J. An Overview of the Global Waste-to-Energy Industry. Waste Management World. 2003, pp. 40–48. Available online: https://waste-management-world.com/artikel/an-overview-of-the-global-waste-to-energy-industry/ (accessed on 30 July 2003).
  121. Kothari, R.; Tyagi, V.; Pathak, A. Waste-to-energy: A way from renewable energy sources to sustainable development. Renew. Sustain. Energy Rev. 2010, 14, 3164–3170. [Google Scholar] [CrossRef]
  122. Khan, I.; Kabir, Z. Waste-to-energy generation technologies and the developing economies: A multi-criteria analysis for sustainability assessment. Renew. Energy 2019, 150, 320–333. [Google Scholar] [CrossRef]
  123. Kalyani, K.A.; Pandey, K.K. Waste to energy status in India: A short review. Renew. Sustain. Energy Rev. 2014, 31, 113–120. [Google Scholar] [CrossRef]
  124. International Renewable Energy Agency (IRENA). Renewable Capacity Statistics. 2022. Available online: https://www.irena.org/publications/2022/Apr/Renewable-Capacity-Statistics-2022 (accessed on 4 February 2023).
  125. Pitt, J.; Heinemeyer, C. Introducing Ideas of a Circular Economy. In Environment, Ethics and Cultures; Brill: Leiden, The Netherlands, 2015; pp. 245–260. [Google Scholar] [CrossRef]
  126. Prieto-Sandoval, V.; Jaca, C.; Ormazabal, M. Towards a consensus on the circular economy. J. Clean. Prod. 2018, 179, 605–615. [Google Scholar] [CrossRef]
  127. Cramer, J. Key Drivers for High-Grade Recycling under Constrained Conditions. Recycling 2018, 3, 16. [Google Scholar] [CrossRef] [Green Version]
  128. Ranta, V.; Aarikka-Stenroos, L.; Ritala, P.; Mäkinen, S.J. Exploring institutional drivers and barriers of the circular economy: A cross-regional comparison of China, the US, and Europe. Resour. Conserv. Recycl. 2018, 135, 70–82. [Google Scholar] [CrossRef]
  129. de Jesus, A.; Mendonça, S. Lost in Transition? Drivers and Barriers in the Eco-innovation Road to the Circular Economy. Ecol. Econ. 2018, 145, 75–89. [Google Scholar] [CrossRef]
  130. Tura, N.; Hanski, J.; Ahola, T.; Ståhle, M.; Piiparinen, S.; Valkokari, P. Unlocking circular business: A framework of barriers and drivers. J. Clean. Prod. 2018, 212, 90–98. [Google Scholar] [CrossRef]
  131. Salim, H.K.; Stewart, R.A.; Sahin, O.; Dudley, M. Drivers, barriers and enablers to end-of-life management of solar photovoltaic and battery energy storage systems: A systematic literature review. J. Clean. Prod. 2018, 211, 537–554. [Google Scholar] [CrossRef]
  132. Agyemang, M.; Kusi-Sarpong, S.; Khan, S.A.; Mani, V.; Rehman, S.T.; Kusi-Sarpong, H. Drivers and barriers to circular economy implementation. Manag. Decis. 2019, 57, 971–994. [Google Scholar] [CrossRef]
  133. Gusmerotti, N.M.; Testa, F.; Corsini, F.; Pretner, G.; Iraldo, F. Drivers and approaches to the circular economy in manufacturing firms. J. Clean. Prod. 2019, 230, 314–327. [Google Scholar] [CrossRef]
  134. Jabbour, C.J.C.; Seuring, S.; de Sousa Jabbour, A.B.L.; Jugend, D.; De Camargo Fiorini, P.; Latan, H.; Izeppi, W.C. Stakeholders, innovative business models for the circular economy and sustainable performance of firms in an emerging economy facing institutional voids. J. Environ. Manag. 2020, 264, 110416. [Google Scholar] [CrossRef]
  135. Dijkstra, H.; van Beukering, P.; Brouwer, R. Business models and sustainable plastic management: A systematic review of the literature. J. Clean. Prod. 2020, 258, 120967. [Google Scholar] [CrossRef]
  136. Jia, F.; Yin, S.; Chen, L.; Chen, X. The circular economy in the textile and apparel industry: A systematic literature review. J. Clean. Prod. 2020, 259, 120728. [Google Scholar] [CrossRef]
  137. Aloini, D.; Dulmin, R.; Mininno, V.; Stefanini, A.; Zerbino, P. Driving the Transition to a Circular Economic Model: A Systematic Review on Drivers and Critical Success Factors in Circular Economy. Sustainability 2020, 12, 10672. [Google Scholar] [CrossRef]
  138. Neves, S.A.; Marques, A.C. Drivers and barriers in the transition from a linear economy to a circular economy. J. Clean. Prod. 2022, 341, 130865. [Google Scholar] [CrossRef]
  139. Neligan, A.; Baumgartner, R.J.; Geissdoerfer, M.; Schöggl, J. Circular disruption: Digitalisation as a driver of circular economy business models. Bus. Strat. Environ. 2022. [Google Scholar] [CrossRef]
  140. Mutezo, G.; Mulopo, J. A review of Africa’s transition from fossil fuels to renewable energy using circular economy principles. Renew. Sustain. Energy Rev. 2020, 137, 110609. [Google Scholar] [CrossRef]
  141. Garrido-Prada, P.; Lenihan, H.; Doran, J.; Rammer, C.; Perez-Alaniz, M. Driving the circular economy through public environmental and energy R&D: Evidence from SMEs in the European Union. Ecol. Econ. 2020, 182, 106884. [Google Scholar] [CrossRef]
  142. Maqbool, A.; Khan, S.; Haleem, A.; Khan, M.I. Investigation of Drivers Towards Adoption of Circular Economy: A DEMATEL Approach. In Recent Advances in Mechanical Engineering; Springer: Singapore, 2020; pp. 147–160. [Google Scholar] [CrossRef]
  143. Curtis, T.; Smith, L.; Buchanan, H.; Heath, G. A Circular Economy for Lithium-Ion Batteries Used in Mobile and Stationary Energy Storage: Drivers, Barriers, Enablers, and U.S. Policy Considerations; (No. NREL/TP-6A20-77035); National Renewable Energy Lab. (NREL): Golden, CO, USA, 2021. [Google Scholar] [CrossRef]
  144. Yildizbasi, A. Blockchain and renewable energy: Integration challenges in circular economy era. Renew. Energy 2021, 176, 183–197. [Google Scholar] [CrossRef]
  145. Mignacca, B.; Locatelli, G. Modular Circular Economy in Energy Infrastructure Projects: Enabling Factors and Barriers. J. Manag. Eng. 2021, 37, 04021053. [Google Scholar] [CrossRef]
  146. International Energy Agency (IEA). The Role of Critical Minerals in Clean Energy Transitions. 2022. Available online: https://www.iea.org/reports/the-role-of-critical-minerals-in-clean-energy-transitions/executive-summary (accessed on 30 January 2022).
  147. Geng, Y.; Zhu, Q.; Doberstein, B.; Fujita, T. Implementing China’s circular economy concept at the regional level: A review of progress in Dalian, China. Waste Manag. 2009, 29, 996–1002. [Google Scholar] [CrossRef]
  148. Xue, B.; Chen, X.-P.; Geng, Y.; Guo, X.-J.; Lu, C.-P.; Zhang, Z.-L.; Lu, C.-Y. Survey of officials’ awareness on circular economy development in China: Based on municipal and county level. Resour. Conserv. Recycl. 2010, 54, 1296–1302. [Google Scholar] [CrossRef]
  149. Zhu, Q.; Geng, Y. Drivers and barriers of extended supply chain practices for energy saving and emission reduction among Chinese manufacturers. J. Clean. Prod. 2013, 40, 6–12. [Google Scholar] [CrossRef]
  150. Vanner, R. Scoping Study to Identify Potential Circular Economy Actions, Priority Sectors, Material Flows and Value Chains. 2014. Available online: http://www.eesc.europa.eu/resources/docs/scoping-study.pdf (accessed on 22 December 2022).
  151. Bicket, M.; Guilcher, S.; Hestin, M.; Hudson, C.; Razzini, P.; Tan, A.; Ten Brink, P.; Van Dijl, E.; Vanner, R.; Watkins, E. Scoping Study to Identify Potential Circular Economy Actions, Priority Sectors, Material Flows and Value Chains. 2014. Available online: https://www.ecologic.eu/14578 (accessed on 22 December 2022).
  152. Gumley, W. An Analysis of Regulatory Strategies for Recycling and Re-Use of Metals in Australia. Resources 2014, 3, 395–415. [Google Scholar] [CrossRef]
  153. Rizos, V.; Behrens, A.; Kafyeke, T.; Hirschnitz-Garbers, M.; Ioannou, A. The Circular Economy: Barriers and Opportunities for SMEs. CEPS Working Documents. 2015. Available online: https://www.ceps.eu/ceps-publications/circular-economy-barriers-and-opportunities-smes/ (accessed on 30 September 2015).
  154. Rizos, V.; Behrens, A.; Van Der Gaast, W.; Hofman, E.; Ioannou, A.; Kafyeke, T.; Flamos, A.; Rinaldi, R.; Papadelis, S.; Hirschnitz-Garbers, M.; et al. Implementation of Circular Economy Business Models by Small and Medium-Sized Enterprises (SMEs): Barriers and Enablers. Sustainability 2016, 8, 1212. [Google Scholar] [CrossRef]
  155. Böttcher, C.F.; Müller, M. Drivers, Practices and Outcomes of Low-carbon Operations: Approaches of German Automotive Suppliers to Cutting Carbon Emissions. Bus. Strat. Environ. 2013, 24, 477–498. [Google Scholar] [CrossRef]
  156. Ilić, M.; Nikolić, M. Drivers for development of circular economy–A case study of Serbia. Habitat Int. 2016, 56, 191–200. [Google Scholar] [CrossRef]
  157. Pheifer, A.G. Barriers and Enablers to Circular Business Models. 2017. Available online: https://www.scribd.com/document/502885354/Barriers-and-Enablers-to-Circular-Business-Models# (accessed on 30 April 2017).
  158. Mont, O. Business Model Innovation for a Circular Economy Drivers and Barriers for the Swedish Industry–The Voice Of Rees Companies. 2017. Available online: https://lup.lub.lu.se/search/ws/files/33914256/MISTRA_REES_Drivers_and_Barriers_Lund.pdf (accessed on 30 January 2017).
  159. Wildschut, D. The need for citizen science in the transition to a sustainable peer-to-peer-society. Futures 2017, 91, 46–52. [Google Scholar] [CrossRef]
  160. Hart, J.; Adams, K.; Giesekam, J.; Tingley, D.D.; Pomponi, F. Barriers and drivers in a circular economy: The case of the built environment. Procedia CIRP 2019, 80, 619–624. [Google Scholar] [CrossRef]
  161. Jabbour, C.J.C.; Fiorini, P.D.C.; Wong, C.W.Y.; Jugend, D.; Jabbour, A.B.L.D.S.; Seles, B.M.R.P.; Pinheiro, M.A.P.; da Silva, H.M.R. First-mover firms in the transition towards the sharing economy in metallic natural resource-intensive industries: Implications for the circular economy and emerging industry 4.0 technologies. Resour. Policy 2020, 66, 101596. [Google Scholar] [CrossRef]
  162. Hammond, Z. Culturally Responsive Teaching and the Brain: Promoting Authentic Engagement and Rigor among Culturally and Linguistically Diverse Students; Corwin Press: Thousand Oaks, CA, USA, 2014. [Google Scholar]
  163. Barrett, J.; Cooper, T.; Hammond, G.P.; Pidgeon, N. Industrial energy, materials and products: UK decarbonisation challenges and opportunities. Appl. Therm. Eng. 2018, 136, 643–656. [Google Scholar] [CrossRef]
  164. Kilgo, M.K.; Anctil, A.; Kennedy, M.S.; Powell, B.A. Metal leaching from Lithium-ion and Nickel-metal hydride batteries and photovoltaic modules in simulated landfill leachates and municipal solid waste materials. Chem. Eng. J. 2022, 431, 133825. [Google Scholar] [CrossRef]
  165. Kuchhal, P.I.Y.U.S.H.; Sharma, U.C. Battery waste management. Environ. Sci. Eng. 2019, 5, 141–155. [Google Scholar]
  166. Mrozik, W.; Rajaeifar, M.A.; Heidrich, O.; Christensen, P. Environmental impacts, pollution sources and pathways of spent lithium-ion batteries. Energy Environ. Sci. 2021, 14, 6099–6121. [Google Scholar] [CrossRef]
  167. Korniejenko, K.; Figiela, B.; Miernik, K.; Ziejewska, C.; Marczyk, J.; Hebda, M.; Cheng, A.; Lin, W.-T. Mechanical and Fracture Properties of Long Fiber Reinforced Geopolymer Composites. Materials 2021, 14, 5183. [Google Scholar] [CrossRef]
  168. Siddique, M.B.M.; Kashem, S.B.A.; Iqbal, A. Biofuels in Malaysian perspective: Debates and benefits. In Proceedings of the 2018 IEEE 12th International Conference on Compatibility, Power Electronics and Power Engineering (CPE-POWERENG 2018), Doha, Qatar, 10–12 April 2018; pp. 1–6. [Google Scholar]
  169. Ruan, R.; Zhang, Y.; Chen, P.; Liu, S.; Fan, L.; Zhou, N.; Ding, K.; Peng, P.; Addy, M.; Cheng, Y.; et al. Biofuels: Introduction. In Biofuels: Alternative Feedstocks and Conversion Processes for the Production of Liquid and Gaseous Biofuels; Academic Press: Cambridge, MA, USA, 2019; pp. 3–43. [Google Scholar]
Figure 1. Framework of literature review.
Figure 1. Framework of literature review.
Energies 16 01779 g001
Figure 2. Distribution of studies based on publication year, 2010–2022.
Figure 2. Distribution of studies based on publication year, 2010–2022.
Energies 16 01779 g002
Figure 3. Main characteristics of the literature. Section “a” shows the share of studies based on their scope of research, while Section “b” shows the number of CE studies in the energy sector.
Figure 3. Main characteristics of the literature. Section “a” shows the share of studies based on their scope of research, while Section “b” shows the number of CE studies in the energy sector.
Energies 16 01779 g003
Figure 4. Circular economy process.
Figure 4. Circular economy process.
Energies 16 01779 g004
Figure 5. Electricity generated by type of waste renewable energy. Source of Data: International Renewable Energy Agency (IRENA) [124], Figures “a”, “b”, “c” and “d” show the generating capacity of power plants using bioenergy, biofuels, renewable waste, and biogas, respectively.
Figure 5. Electricity generated by type of waste renewable energy. Source of Data: International Renewable Energy Agency (IRENA) [124], Figures “a”, “b”, “c” and “d” show the generating capacity of power plants using bioenergy, biofuels, renewable waste, and biogas, respectively.
Energies 16 01779 g005
Figure 6. Global electricity production by source of fuel. Source of Data: International Renewable Energy Agency (IRENA) [124].
Figure 6. Global electricity production by source of fuel. Source of Data: International Renewable Energy Agency (IRENA) [124].
Energies 16 01779 g006
Table 1. Circular economy literature.
Table 1. Circular economy literature.
IndustrySample of Publications
Supply ChainDe Angelis et al., 2018 [30]; Farooque et al., 2019 [31]; Hussain & Malik, 2020 [32]; Kumar et al., 2021 [33]
Agri-foodToop et al., 2017 [34]; Esposito et al., 2020 [35]; Gkountani et al., 2021 [36]; Liu et al., 2021 [37]
Energyvan Leeuwen et al., 2018 [38]; Priyadarshini & Abhilash, 2020 [39]; Holmberg & Ideland, 2021 [40]
Fashion & Textilesde Aguiar et al., 2021 [41]; Radhakrishnan, 2021 [42]; Chen et al., 2021 [43]
ManufacturingPaletta et al., 2019 [44]; Acerbi & Taisch, 2020 [45]; Badhotiya et al., 2022 [46]
Furniture & WoodSusanty et al., 2020 [47]; Hartini et al., 2021 [48]; Paul et al., 2022 [49]
WaterAyçin & Kayapinar Kaya, 2021 [50]; Liu et al., 2021 [51]; Salminen et al., 2022 [52]
PlasticSimon, 2019 [53]; Guyot Phung, 2019 [54]; Alvarez-Risco et al., 2020 [55]
PublicKlein et al., 2020 [56], Barreiro-Gen & Lozano, 2020 [57]; Droege et al., 2021 [58]
AutomotiveSaidani et al., 2018 [59]; Kayikci et al., 2021 [60]; Sopha et al., 2022 [61]; Baldassarre et al., 2022 [62]
ConstructionJones and Comfort, 2018 [63]; Bilal et al., 2020 [64]; Hjaltadóttir & Hild, 2021 [65]; Giorgi et al., 2022 [66]
TourismBrightley, 2017 [67]; Falcone, 2019 [68]; Vatansever et al., 2021 [69]; Kazancoglu et al., 2021 [70]
MiningKinnunen & Kaksonen, 2019 [71]; Singh et al., 2020 [72]; Gedam et al., 2021 [73]; Luthra et al., 2022 [74]
ElectronicGama et al., 2016 [75]; O’Connor et al., 2018 [76]; Curtis et al., 2021 [77]; Rizos & Bryhn, 2022 [78]
CoffeeVan Keulen & Kirchherr, 2021 [79]; Pires, 2022 [80]
LeatherMoktadir et al., 2020 [81]; Karuppiah et al., 2021 [82]; Cabrera-Codony et al., 2021 [83]
LogisticsVan Buren et al., 2016 [84]; Dutta et al., 2021 [85]; Gupta & Singh, 2021 [86]
FinanceHassan et al., 2020 [87]; Gonçalves et al., 2022 [88]
MedicalMacNeill et al., 2020 [89]; Kandasamy et al., 2022 [90]
MaritimeLaso et al., 2018 [91]; Milios et al., 2019 [92]; Okumus et al., 2022 [93]
AerospaceStavileci & Andersson, 2015 [94]; Brennan & Vecchi, 2020 [95]; Dias et al., 2022 [96]
CosmeticFortunati et al., 2020 [97]; Lourenço-Lopes et al., 2020 [98]; Morea et al., 2021 [99]
Table 2. CE drivers at global market.
Table 2. CE drivers at global market.
FactorDrivers
Environmental
  • Developing a circular and sustainable economy is a strategic approach to protecting the environment through waste reduction.
  • CE has the potential to increase the availability and efficiency of resources.
Technical
  • New technologies that facilitate resource optimisation, re-manufacturing and re-generation of products.
  • The potential to improve existing operations.
Economic-Financial
  • To increase profits and market share, industries would adopt CE initiatives that have the potential to reduce costs, boost efficiency, generate new revenue streams, and improve profitability.
  • Through CE, industries can reduce production waste, that can boost profit margins, enhance customer loyalty, entice new customers, and boost investment return.
  • Increasing the long-term revenue generation by recycling activities.
  • There is potential for entrepreneurship, innovation, business development, and synergistic relationships.
  • CE’s potential for economic development and job creation goes beyond profit margins and cost savings.
Institutional-Regulatory
  • Developing regulations and standards associated to recycling and circular economy.
  • Establishing rules and standards by government authorities to support and promote more sustainable production and the use of recycled products.
  • End-of-life management policies to protect resources, safety, health, and environment.
  • Through support funds, credits, and loans, the government can assist enterprises in transitioning from linear to circular pathways.
Social-Cultural
  • Creating a country with minimal waste-related health and environmental problems is a desired goal of governments and societies. CE has the potential to alleviate landfill, solid waste, and emissions by performing functions that include reusing, reprocessing, and recycling waste.
  • Increasing global awareness of sustainability that is connected to social awareness, environmental literacy, and shifting consumer preferences (e.g., from ownership of assets to services models).
  • Consumers are empowered to make environmentally responsible decisions. By increasing consumer awareness of the environmental impact of their purchasing decisions, waste can be significantly reduced.
Health
  • Traditional economies dump substantial amounts of the waste directly or indirectly into the environment, posing a threat to animal and human health. Shifting from a linear to a circular pathway will provide ample opportunity to improve health.
  • The development of circular products with minimal environmental impacts can reduce greenhouse gas emissions and preserve ecosystems.
Supply-chain
  • A reduction in supply dependence and the prevention of high and volatile prices are potential advantages.
  • Resources and capabilities are more readily available due to multidisciplinary.
Organizational
  • Potential for differentiation and strengthening the company brand.
  • Enhancing knowledge about the demands of sustainability.
  • The circular strategy is integrated into the company’s strategy and goals.
  • Increasing the level of knowledge, skills and capabilities for the CE.
Table 3. Barriers to the CE implementation in global markets.
Table 3. Barriers to the CE implementation in global markets.
ClassificationsObstacles
Economic & Financial Obstacles
  • Large capital requirements, high initial costs and uncertain return/profit—CE processes are expensive, so they are not widely adopted. Economies must bear significant up-front costs and risks in the short term—e.g., upgrading machinery, relocating, and shifting factories, creating new distribution and logistics systems, recruiting skilled and professional employees, and training staff. Developing a strong business case will be necessary before transforming a country’s economy toward a CE.
  • Lack of financial support and tax incentives—the CE Adoption is hampered by financial barriers, difficulties in funding CE business models, and high up-front investment costs.
Knowledge Barriers
  • Lack of knowledge that is necessary as a part of the transition towards a circular economy. In order to switch from linear to circular, it is necessary for us to know how and what the necessary steps are. However, given the novelty, complexity, and disruptive nature of the CE, it appears that people lack the proper knowledge. The lack of awareness of the benefits of circular economies has been identified as a barrier to implementing circularity. Following a review of the literature, knowledge gaps have been determined based on five aspects: relatability, transition, validation, product life-cycle analysis, and awareness.
Political Obstacles
  • Lack of knowledge about circularity in the energy sector—due to the political pressure on ending fossil fuel use and raising green energies consumption, researchers are developing more cost-effective methods for generating and distributing renewable energy. However, governmental authorities and political parties face challenges in involving citizens and businesses in the transition toward renewable energy by focusing on the CE in the energy sector. In consequence, the circular transition does not receive much political attention.
Technical Barriers
  • Lack of technical support and training about the CE concept.
  • A shortage of qualified and technical labour forces.
  • Lack of data and information.
  • Infrastructure and development models that require many resources—the traditional model relies on massive growth in industry and infrastructure that is resource-intensive. It is clear that emerging economies require a less resource-intensive development model, but there are no ready-made options.
  • Lack of IT-based measures and monitoring systems—even though specific waste detection software exists, it has not reached every business or has not been used because waste stream data are scarce. Moreover, IT systems are essential for a transition from a physical-goods-based economy to a service-based economy and a less resource-intensive immaterial economy.
Cultural Barriers
  • Cultural challenges—cultural barriers concern aspects of the social, behavioural, and managerial contexts where the CE needs to develop, including the entrenched nature of the linear economy; ownership and status perspectives; and silo mentality.
  • Lack of consumer interest/awareness—the principles of the CE are not yet well known in society. Lack of interest, knowledge, skills, and engagement throughout the value chain by suppliers, customers, and internal is a core cultural barrier to engage with the CE adoption and collaboration in the value chain.
  • Insufficient demand in the market for recycled, remanufactured, or reused products.
  • Hesitant company culture—lacking policies in support of a CE transition and obstructions in laws and regulations of economies.
Regulatory Barriers
  • Lack of regulatory support—the absence of policies in support of the CE transition and obstructions in laws and regulations of economies could pose substantial obstacles to transferring from linearity to circularity in economies.
  • A lack of policies, taxes, and subsidies that support the transition to CE—the government support and financial aid supporting linear production methods pose major obstacles to improving the financial competitiveness of a CE.
Table 4. Recommendations and solutions.
Table 4. Recommendations and solutions.
GroupsRecommendations
Political
  • Policies relating to renewable energies should be sustainable from an environmental perspective. Biofuels must contribute positively to lowering CO2 emissions, protecting water and land resources from depletion and contamination, and protecting the environment.
  • Subsidies to encourage excessive resource consumption should be eliminated, and all ‘externals’ should be incorporated into energy and resource prices for the market to respond effectively.
  • Governments should prohibit producing biofuels that jeopardise the supply of food and crops essential for animal feed and humans. In addition, importers and exporters of biofuels should be aware of and follow all environmental laws and biofuel standards. Biofuel regulations must be aligned with food security policies that protect poor and food-insecure economies. In particular, there should be a focus on the challenges caused by rising food prices in countries heavily reliant on imported foods, particularly among developing countries and vulnerable rural consumers.
Financial
  • The implementation and development of CE programs require financial resources, which means companies need access to a variety of funding options. The most effective way to lead industries towards a CE is through collaboration within the industry value chains as well as establishing financial instruments for investment across all industrial chains at the macro level rather than in a single industry. Consequently, risks and profits can be distributed, and collaboration opportunities can arise to establish a circular economy that is profitable for all sectors.
Technology
  • Implement circular design principles to make future energy infrastructure more durable, repairable, and recyclable.
Political
  • Governments play a critical role in facilitating the transition towards circularity, and insufficient regulations and policies substantially impact the transition from a linear economy to a circular one. As a result, it can be argued that a progressive legal framework and thoughtful principles could facilitate CE adoption.
  • Implementing transparent, robust, and predictable policy frameworks will encourage investments by industries in CE systems.
  • Governments and policymakers must accelerate the transition to CE approaches while addressing global challenges like climate change and water scarcity. These include legislative measures as well as voluntary actions by stakeholders. In order to optimize the treatment and management of resources and waste streams, policy gaps and market barriers must also be addressed.
  • Economies must refrain from dumping unsuitable technologies in third-world countries and exporting machinery and equipment to countries with inadequate waste-management strategies.
Production
  • Resource-efficient manufacturing practices and optimal logistics approaches must be integrated into all industrial policies.
  • Decommissioned equipment can be remanufactured and reused by industries for lower-tier applications.
Social
  • A positive public perception of sustainable practices has a large influence on their behavior, which can motivate industries to revise their business models to promote circularity. In spite of this, due to the relative novelty of CE practices and the existence of linear economic systems in most industries, there is a lack of education relating to CE practices. Given that CE is a novel concept, companies tend to avoid high risks by taking small, safe steps rather than undertaking a complete transformation toward circular approaches. In order to embrace both individuals and industries about circular economic system, knowledge and comprehension need to be cultivated. Through education and media coverage, governments can increase public awareness of circular economies.
Waste Recycling
  • Implement a waste management plan for end-of-life infrastructure by adopting appropriate processing methods.
  • The number of materials and components that can be recycled should be maximized in order to generate secondary raw materials for new energy infrastructures and other manufacturing sectors.
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Ghazanfari, A. An Analysis of Circular Economy Literature at the Macro Level, with a Particular Focus on Energy Markets. Energies 2023, 16, 1779. https://doi.org/10.3390/en16041779

AMA Style

Ghazanfari A. An Analysis of Circular Economy Literature at the Macro Level, with a Particular Focus on Energy Markets. Energies. 2023; 16(4):1779. https://doi.org/10.3390/en16041779

Chicago/Turabian Style

Ghazanfari, Arezoo. 2023. "An Analysis of Circular Economy Literature at the Macro Level, with a Particular Focus on Energy Markets" Energies 16, no. 4: 1779. https://doi.org/10.3390/en16041779

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop