Abstract
The growth in global production and consumption rates has resulted in increased pollution generation by industrial companies. To this end, cleaner production is one of the most widely used strategies to reduce the environmental impacts of industry and gain competitive advantage. However, it is still adopted slowly in many places. Therefore, the objective of this study is to propose a framework composed of governmental, scientific, and industrial strategies, policies, initiatives, and research opportunities for the development of cleaner production. The best practices of the top countries in the cleaner production technical-scientific scenario and the main implementation challenges and opportunities for its scientific development were identified and were the reference for the framework proposals. In the government sector, the framework suggests actions to encourage the adoption of cleaner production practices through national policies, legislation, tax incentives, and educational campaigns. In the scientific sector, it suggested the development of studies about the factors that motivate its adoption, studies about clean technologies, and studies about the cleaner production implementation difficulties. In the industrial sector, it highlighted the importance of the engagement of upper management to focus on efforts to increase the efficiency of manufacturing processes with the adoption of clean technologies, management systems, strengthening of the research and development areas, and replacement of hazardous raw materials. Thus, this study contributes with initiatives that will help the implementation of cleaner production practices, reducing the generation of pollution in industry, increasing the efficiency of its processes, and aligning countries and societies to sustainable development.
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Introduction
Environmental issues came to the spotlight in international agenda at the end of the twentieth century (Khalili et al. 2015; Kubota and Cantorski 2013). In this period, important technological, scientific, and industrial advances occurred and countries like the USA, China, and Germany reached high levels of industrial development (Kan et al. 2012; Ashton et al. 2017). However, the depletion of natural resources, high levels of pollution, and global warming were some of the negative impacts resulting from this scenario (UNIDO/UNEP 2015).
Different studies, such as Orhan et al. (2021) and Soylu et al. (2021), have identified a positive correlation between CO2 emissions, environmental degradation, economic growth, trade openness, and energy use in many countries during the last decades, demonstrating a negative impact on the environment due to the intensive economic advancement. Therefore, the international awareness of the damage caused by companies has also grown (Severo et al. 2017). The environmental management importance has gained strength due to increased social and governmental pressures. Countries’ environmental policies have become increasingly stringent, requiring corporations to adopt initiatives to minimize their environmental impacts (Zhang et al. 2013; Yilmaz et al. 2015).
The Rio Declaration and Agenda 21 formalized sustainable development (SD) as an objective of the international community in the 1990s. The SD expresses the importance of harmonious development on social, economic, and environmental spheres, emphasizing the dependence relationship between them (Zilahy et al. 2009; Khalili et al. 2015). Thus, economic growth should not result in the natural resource depletion and environmental destruction but should guarantee the next generation survival while reducing poverty at world levels (Henriques and Catarino 2015; Khalili et al. 2015).
Therefore, several international institutions have taken actions to promote SD (Zou et al. 2017), especially in industrial companies. The industry is an important sector for several countries’ economies, being one of those responsible for economic growth. However, its manufacturing processes have a significant impact on pollution levels and environmental degradation (Huang et al. 2013; Jia et al. 2014; Silvestre and Neto 2014). Thus, several solutions and technologies were developed to reduce environmental impacts of industrial activities (Faé Gomes et al. 2013; Khalili et al. 2015; Hens et al. 2018).
Among these solutions, cleaner production (CP) is a strategy used by many industrial company managers as a mechanism to promote processes less polluting (Ashton et al. 2017; Kubota and Cantorski 2013; Neto et al. 2016). The United Nations Environment Programme (UNEP) conceptualized CP in 1989 as the continuous application of a preventive and integrated environmental strategy to processes, products, and services, with the objective of increasing companies’ overall efficiency and reducing risks to humans and the environment (Yusup et al. 2014; Nemet et al. 2016; Hens et al. 2018).
In the subsequent years to the CP conceptualization, UNEP, in partnership with the United Nations Industrial Development Organization (UNIDO), developed several projects to demonstrate the applicability of this strategy in developing countries. These projects culminated in the creation of the National Cleaner Production Centers (NCPC) program in 1995. These centers were established in developing countries in partnership with local organizations. They have the mission to facilitate international collaboration among companies around the world, share knowledge, experiences, and discoveries on techniques and practices for the use of clean technologies, and provide support to organizations on CP adoption (Severo et al. 2015; UNIDO; UNEP 2015). Those centers offer services to raise awareness of the benefits and advantages on adopting CP; develop CP projects to demonstrate its environmental, financial, and social benefits; help obtain financing; provide policy advice to national and local governments; and disseminate technical information (UNIDO 2021).
From 1995 to 2015, NCPCs were opened in more than 58 countries, where they supported numerous CP implementations and tracked their results. The centers have accumulated great experience since their creation and are currently one of the main institutions fostering the expansion of CP practices in the world (UNIDO; UNEP 2015).
CP allows the waste reduction through more efficient processes because it reduces the use of resources and the pollution generation, improves the company image, increases employee satisfaction levels due to positive impacts on health and safety, and reduces the productive systems’ operating costs, increasing economic performance, and leveraging the companies’ profits (Aparecido et al. 2013; Ashton et al. 2017; Gonçales Filho et al. 2018).
CP integrates waste management with pollution prevention, seeking the creation of environmentally and socially friendly production processes. It can be developed in two ways: implementing clean technologies to processes that result in lower environmental impacts and improving existing processes efficiency (Huang et al. 2013; Campos et al. 2020).
Therefore, clean technology (CT) development and improvement are important factors in CP implementations. Technological improvements have great potential to reduce environmental impacts on manufacturing processes, favoring more ecologically efficient methods and equipment, reducing the use of energy, water, and raw materials, and improving productivity (González 2005; Hall and Helmers 2013; Pinkse and Dommisse 2009).
The CP practice implementation can be done on three levels, according to Figure 1 (Gonçales Filho et al. 2018).
In Figure 1, it is possible to observe that CP aims to eliminate and minimize industrial waste and emissions with three-level actions. Level 1 is composed of source reduction strategies, and internal recycling actions compose level 2. Waste reduction in its source can be achieved by modifying the product or process. The product can be designed to minimize negative impacts on the environment during its life cycle and process modifications can be done through housekeeping, replacing raw material, or promoting technological changes in the manufacturing process. The third level is based on waste reuse strategies as external recycling and biogenic cycles (Espuny et al. 2021; Gonçales Filho et al. 2018).
However, there are challenges to implement CP. External factors such as instability in the political, economic, and market sectors cause insecurity to companies, which become reluctant to invest in its adoption (Dobes 2013; Gonçales Filho et al. 2018). Internal factors such as lack of leadership and senior managers inexperience with CP, lack of monitoring and reviews of implementations, and use of old and inefficient technologies hinder the success of CP practices. Inefficient communication, insufficient employee training, a lack of knowledge about clean technologies, lack of employee involvement, and resistance to change are also internal barriers faced by companies during CP adoption (Aparecido et al. 2013; Khalili et al. 2015; Gonçales Filho et al. 2018).
The need to overcome these barriers highlights the importance of studies that identify and propose initiatives that can be incorporated into CP adoption efforts to stimulate its use. Government, industry, and academia are the sectors with the most important roles in solving the countries’ environmental problems. Their efforts and initiatives when focused on CP dissemination are catalysts for its development (Khalili et al. 2015). The triple helix model (Fig. 2) points out these sectors as the innovation main generators and responsible for driving sustainable economic development in modern societies, including CP solution creation (Kimatu 2016).
The triple helix is a concept that incentivizes innovation through closer relations between the “actors” university, organizations, and government. The mentioned actors should strengthen their institutional relations in order to foster a technological pole, discussing the main obstacles and opportunities for economic development, defining their roles to achieve this goal. Usually, this procedure is articulated at a regional level, through the establishment of growth agreements, or even through the formation of municipal technology councils. The results that are usually expected are the construction of new facilities by the public authorities; improvement of students by the universities; and negotiation of new supplier relationships, articulating competitive supply chains. This initial interaction, when well-organized, provides better industry outputs and improves the local economy (Etzkowitz, 2008). As examples of development based on the triple helix, one can cite the partnership between Stanford (university), Silicon Valley (government), and Google, Apple, and Facebook (companies) in San Francisco (USA), developing a strong technology industry. In Brazil, one can cite examples from São José dos Campos, involving the Institute of Aerospace Technology (university), Air Force (government), and Embraer (organization) in São José dos Campos, developing a recognized aviation industry (Baptista et al. 2020; Pique et al. 2020).
The government is responsible for regulating relations between these sectors, creating partnerships, promoting research, and ensuring the necessary infrastructure for companies. The industry generates employment and income and is responsible for the strategic demands of innovation, which can be developed internally by its research and development (R&D) departments or through partnerships with the other two sectors. Universities, on the other hand, are responsible for the education and training of professionals, and for the new products, ideas, and innovations of R&D (Kimatu 2016; Leydesdorff and Etzkowitz 1996; Leydesdorff and Meyer 2006).
The government, industry, and university are responsible for identifying sustainable initiative opportunities. They should be prepared and motivated to assume their responsibilities in promoting SD by encouraging and developing sustainable policies, adopting environmental objectives and strategies in their economic, environmental, and social spheres, and disseminating their actions and results transparently (Almeida et al. 2015; Ashton et al. 2017; Vieira and Amaral 2016). Thus, these sectors CP’s incentive initiatives contribute to countries’ SD.
Thus, considering the theme importance, 31 reviews of CP have been published in the last 5 years. Among the most cited works, Dong et al. (2019) present new perspectives on cleaner production in mines, to eliminate waste in dams. Wang et al. (2017) review the reduction of technological impacts on rare earth element extraction in China. Vieira and Amaral (2016) identified the main issues that prevent the wider implementation of cleaner production. Tiwari et al. (2016) analyzed solid waste that could replace concrete in civil construction activities, and Hoyos-Martínez et al. (2019) studied the production of tannins in nature, highlighting the main positive and negative impacts.
However, despite the contributions of these reviews to the CP improvement, they are restricted to specific areas and do not consider the potential of coordinated actions from governments, companies, and universities to CP development. Thus, this study is different from prior studies because it adds contributions from the triple helix’s sector perspectives by means of the study of innovations and patents; business initiatives; white papers; university initiatives; and researchers’ initiatives. The diversity of data sources and the authors’ contributions allowed a review of scientific and technical content simultaneously, resulting in a broader and more detailed understanding of the subject. Thus, this work makes it possible to fill scientific gaps related to the need for identification of the main factors that motivate the various sectors of industry and society to adopt CP (Wesseh Jr and Lin 2015; Severo et al. 2017; Hens et al. 2018), and the identification and proposal of solutions to the main difficulties faced by companies during the CP implementation (Severo et al. 2015; Govindan et al. 2016; De Oliveira et al. 2016).
Therefore, the research question posed in this study is: how it is possible to promote cleaner production initiatives to contribute to sustainable development? Answering this research question, this article has the objective of proposing a CP development framework composed of policies, strategies, initiatives, and research opportunities to be developed by the governmental, industrial, and academic sectors, filling the gap of prior studies by bringing a broader view of CP’s technical and scientific potential to contribute to SD. The CP policies, strategies, and initiatives that were prominent in the top countries of the CP technical-scientific scenario and the main CP implementation challenges and opportunities identified in the literature were analyzed and adapted in light of the authors’ expertise, serving as a benchmark for the framework proposals. It is expected that the public sector, business organizations decision-makers, and academic institutions can use the framework to guide their scientific, technological, public, and private initiatives and investments aiming the CP development and, consequently, contribute to SD.
The article is organized into 5 sections, considering this introduction. In the second section, the research method and its stages are described, in the third section, the research results are presented and discussed, in the fourth section, the CP development framework is presented and discussed, and in the fifth section, the authors’ conclusions are presented, followed by the references.
Research method
The research that originated this article was conducted according to the flow of activities presented in Figure 3.
The research was conducted in five phases: (1) objectives and method definition; (2) research criteria, data collection, and organization; (3) CP technical-scientific scenario mapping; (4) CP framework elaboration; and (5) conclusion. Table 1 describes all the phases and stages of this research.
This research can be classified as having a descriptive and analytical objective, with an applied nature, a qualitative approach, and as experimental research. The descriptive objective consists of describing the state of a theme at the moment of research realization, and the analytical objective consists in using the facts or information available for developing analyses. The nature is applied, because the research seeks a solution to a socioeconomic problem. The approach is qualitative because the research is focused on the investigation of concepts associated with the CP field of study, seeking an in-depth conclusion about good initiatives that can be adopted by industries, governments, and universities to develop CP. Finally, the research can be considered experimental because the authors raised information that would allow them to answer the research question (Kothari and Garg 2019).
Thus, at the end of this study, a framework was proposed for the CP development consisting of suggestions of policies, strategies, initiatives, and research opportunities to be developed by governments, industries, and universities. The initiatives mapped in the CP technical-scientific scenario and the opportunities and challenges identified in the theme’s literature were analyzed and adapted in the light of the authors’ expertise and served as a benchmark for the framework proposal (Figure 4).
Results and discussion
Technical-scientific scenario
This topic presents the main CP actions, achievements, initiatives, and policies adopted by their governments, industries, and scientific communities of the countries that stand out in the CP technical-scientific scenario. From the ten most cited countries in the CP area, the four with the highest h indexes (Brazil, China, the USA, and Malaysia) were analyzed. These countries are references in academic-scientific terms due to the initiatives mapped and, therefore, will serve as a basis for the framework to promote this strategy.
Brazil
Brazil is the country with the highest h-index (16) on the theme. It was one of the thirteen countries, with China, Croatia, the Czech Republic, Hungary, India, Mexico, Nicaragua, Slovakia, Tanzania, Tunisia, and Zimbabwe, which received the first NCPCs. The National Center of Clean Technologies was founded in 1995, with the support of the National Industrial Learning Service of Brazil. This center was responsible for creating the Brazilian Cleaner Production Network (BCPN) in partnership with the Brazilian Business Council for Sustainable Development. This network is composed of organizations and professionals dedicated to accelerating the transfer of information and CT among companies in the country, and provides specialized services in CP (Kist et al. 2009; Pereira and Sant’Anna 2012; UNIDO; UNEP 2015).
BCPN has created a guide for the implementation of CP practices on Brazilian companies. A methodology divided into 5 phases was proposed: planning and organization, pre-assessment, evaluation, feasibility study, and implementation (CNTL et al. 2003).
Another important initiative was the structuring of CP state forums made by the Brazilian government with the purpose of articulating a national CP policy (Brazil 2006). In 2011, the first Brazilian national policy based on CP aspects was created: The Action Plan for Sustainable Production and Consumption.
The policy’s action plans foster sustainable policies, programs, and initiatives with the objective of improving the solutions to Brazil’s socio-environmental problems. Actions and targets have been defined segmented into 4-year cycles starting in 2011, in the areas of education, public policies, solid waste recycling, sustainable retailing, sustainable construction, and sustainable industry, to encourage the adoption of pollution prevention practices (Brazil 2011). Implementation strategies are redefined at the end of each cycle according to the evolving needs of the Brazilian economy.
The first cycle (2011 to 2014) actions focused on the dissemination of sustainable consumption and production culture. Different training and qualification processes were conducted on the subject. A Public Administration Environmental Agenda was created, resulting in an investment of USD 3.53 billion in solid waste plans and infrastructure, while several programs and partnerships between the public and private sector were formed (Brazil 2014). The actions of the second cycle of implementation (2016 to 2020) will only be published in 2021.
The Brazilian academic-scientific community stands out for developing internationally influential works on CP. Brazil obtained the highest number of citations (548) between 2014 and January 2020 at Scopus. Articles by Brazilian authors and universities are also among the most cited worldwide in this theme, which will be presented next.
Among the 10 most cited authors about CP, six are Brazilian. Among the 30 most cited articles on CP between 2014 and January 2020, six of them are authored or coauthored by any of these authors. Prof. Dr. Severo, Prof. Dr. Dorion, and Prof. Dr. de Guimarães studied the joint application of CP with environmental management practices in Brazilian companies and their respective impacts on organizational performance in the 5th and 8th most cited articles (Severo et al. 2017, 2015). Prof. Dr. Ometto studied the impact of ISO 14001 on CP practices in the 20th most cited article (De Oliveira et al. 2016) and the implementation of best practices in a paper production process in the 28th most cited article (Silva et al. 2015). Finally, Prof. Dr. Agostinho and Prof. Dr. Giannetti performed the analysis of the articles published in the international workshop on advances in CP in the 9th and 27th most cited articles (Almeida et al. 2015, 2017).
Prof. Dr. Giannetti, B. F has extensive experience in this field of study. He is the co-founder of the Advances in Cleaner Production Network, an international forum for the exchange of information and research results about CP technologies, concepts, and policies (ACPN 2020). Giannetti also composes the editorial board of the Journal of Cleaner Production (JCP) and is the associate editor of the Journal of Environmental Accounting and Management (FAPESP 2020).
Regarding the 10 most cited teaching and research institutes in the CP area and ordered according to their H-index, 4 are Brazilian. Among them, UNIP stands out because it has the Production and Environment Laboratory (LaProMA) dedicated to CP studies (UNIP 2020). LaProMA is one of the founders and organizers of the International Workshop on Advances in Cleaner Production in collaboration with the JCP that is one of the largest international events in this area and occurs annually, bringing together some of the leading researchers on the subject.
However, despite the Brazilian government initiatives to promote and develop the CP and the prominence of Brazilian researchers in the global context, there is a lack of integration between the universities and government, and a notorious absence of public policies that encourage the adoption of this strategy. This fact has generated few practical results regarding the CP adoption by Brazilian companies and few partnerships between universities/research centers and companies (Neto et al. 2016; Pereira and Sant’Anna 2012). Therefore, Brazil develops less technologies than the innovation leading countries in CP area, what can be seen in the number of priority patents related to CT registered in the country.
Brazil is not among the 15 countries that most develop patents in this area (Figure 5), showing that, although it stands out in other CP aspects, the country is still far from those at the top of this ranking. Brazil registered 89 patents during the studied period, 500 times fewer patents than China and 200 times fewer than the USA. The two most recent patents registered by inventors in Brazil, with the term cleaner production, were “Thermo Insulating Concrete” and the patent “Production of ceramic proppant from iron ore and/or waste rock from its exploitation and/or tailings from its beneficiation with the agglomeration of fine and ultrafine particles”.
The patent “Thermo Insulating Concrete” is an invention that includes glass fiber rejects in concrete intended for construction. The thermal insulating performance is superior to conventional concrete. Thus, it is possible to reduce the use of natural aggregates in the production of concrete, allowing the reuse of waste that would otherwise be sent to landfills. This patent decreases the negative environmental impacts and reduces the cost of waste treatment for municipalities and organizations (Mendes et al. 2018).
The patent “Production of ceramic proppant from iron ore and/or waste rock from its exploitation and/or tailings from its beneficiation with an agglomeration of fine and ultrafine particles” is a process of ceramic proppant that allows the agglomeration of several products and by-products of the ore—including tailings—forming a ceramic product with high added value. This invention allows the reduction of tailings in dams, avoiding damage to the environment and saving financial and natural resources (Da Silva and Januario 2021).
Therefore, although the Brazilian academic-scientific community is globally known for its work in the CP area, there is a lack of effective initiatives to promote its adoption in public and private organizations and initiatives to encourage the development of clean solutions and technologies in the country. Therefore, the Brazilian government should encourage the R&D of clean technologies, implement taxes for the most polluting economic sectors of the country, subsidize the development of innovations and patents, and promote public-private partnerships between companies, research centers, and the government (Adebayo et al. 2021a, 2021b).
China
China has the second-largest h-index on the subject (14). Its intense industrialization process has generated severe environmental problems (Peng and Liu 2016). Air pollution, biodiversity losses, soil pollution, water pollution, water scarcity, and high waste generation have caused serious economic losses, social damage, and high health costs in China (Soylu et al. 2021; Kan et al. 2012; Li et al. 2014; Liu and Diamond 2005; Lu et al. 2015).
The Chinese government began an intense process to combat pollution due to the seriousness of the environmental crisis in the country (Liu and Diamond 2005). China invested USD 378.5 billion in 16 sustainability programs between 1978 and 2015, most of it in the last 20 years (Jingtao 2019). To make its energy matrix cleaner, China was the country that most invested in renewable energy between 2010 and 2019 in the world (Ajadi et al. 2019).
Therefore, CP was an important solution for the prevention and reduction of environmental impacts generated by Chinese industries (Peng and Liu 2016). To expand and intensify the CP adoption, several government agencies have promoted research on the subject (Changbo et al. 2015).
China received one of the first NCPCs. The Chinese government has been promoting the opening of Regional Cleaner Production Centers and Enterprise Cleaner Production Centers since 1994 spreading these strategy practices throughout the country. At least 22 CP centers were opened in several provinces until 2012, which played an important role in the search for SD in China (Changbo et al. 2015; Peng and Liu 2016; UNIDO; UNEP 2015).
Between 1992 and 2002, the Chinese government enacted laws regulating and encouraging CP adoption among its companies. The 2002 CP Promotion Law stands out as the first CP-specific legislation adopted by a developing country (Changbo et al. 2015; Shi et al. 2008).
In this law, several policies were defined aiming for the inclusion of CP practices in national plans and programs through tax incentives, support to research and clean technology development, and partnerships with international institutions (Cleaner Production Promotion Law 2002). The CP application has proven to be more efficient than conventional end-of-pipe approaches to pollution control in the country (Shi et al. 2008).
The CP Promotion Law established mandatory audits for three categories of companies: companies that exceeded the national and local pollution generation standards, companies where the rate of energy consumption per unit produced exceeded the limits defined by the government, and all companies that used or produced toxic and hazardous materials. Thus, as opposed to the strategies of most other countries where CP had been promoted voluntarily, mandatory audits became the focus of Chinese pollution response policies (Bai et al. 2015; Peng and Liu 2016; Zhang et al. 2013).
Thus, China is a successful case in the adoption of CP practices among developing countries (Peng and Liu 2016). The CP advances in the country warm the attention of the world academic-scientific community, where Chinese works have been the most cited in recent years (565 quotes).
Three of the 30 papers analyzed have Chinese authors’ participation. Wesseh Jr and Lin (2015) developed an optimization model to estimate the optimal amount to be invested by the government of Liberia in the research and development of renewable energy technologies in order to drive replacement of fossil fuel use, reduce the environmental costs of the country’s economic development, and reduce greenhouse gas emissions. Jia et al. (2014) developed an assessment indicator framework for the industry of vanadium extraction from stone coal for assessing the cleaner production process. Finally, Long et al. (2014) designed and constructed a novel plant in pilot scale for fabric rope dyeing with supercritical carbon dioxide fluid for cleaner production of textiles. The plant and application processes designed are water and effluent free and allow energy conservation, being environmentally friendly in comparison with conventional dying processes.
Among the 10 most cited institutes in the articles published by its researchers in this area, 2 are Chinese: Ministry of Education and Wuhan University of Technology (WUT). WUT is a reference in research in China, with 34 research centers. Engineering, materials development, logistics, mechatronics, information technology, and environmental technology laboratories are among the centers developed by the Chinese government. Simultaneously, the university has about 230 research centers in partnership with local companies (Wuhan University of Technology 2020).
All investment from research institutions and the Chinese government has reflected on the level of CT development in the country. China is the country with the most patents registered (Figure 5), 51,888, 2.8 times more than the USA, which is the second country with most patents in this area (18137). The latest patents filed in China were “Notification method for refrigerator, appliance, and refrigerator” and “Improved label fabric coating and manufacturing method”.
The patent “Notification method for refrigerator, appliance, and refrigerator” is an application used in smart appliances, enabling a database that stores the technical information of the food that is packed inside. In this way, the foods are controlled and users are notified of their expiration. This application can be used in foodservice establishments, such as restaurants and bars, and the food industry, improving cost management and reducing waste generation (Fei et al. 2019).
The patent “Improved label fabric coating and manufacturing method” is a method to improve the quality of the labels that are sewn onto clothes, using a comfortable, practical, and consumer-friendly material. A printer is used to produce these labels, saving all the tasks of the fabric industry, such as designing, weaving, coating finishing, and organic solvents. To achieve these results, this invention relies on soft-coated tape that does not irritate the skin, wash protection, clearly printed material, and good readability, among other attributes (Hong et al. 2021).
Therefore, driven by the pressures of their country’s serious socio-environmental problems, the Chinese government and society have been adopting initiatives to promote the reduction of pollution generated by their industries, to increase the environmental efficiency of their companies and to adopt a clean energy matrix (Hong and Li 2013). Those many initiatives to promote sustainable practices and partnerships between the Chinese government, industry, and academia have generated important achievements and advances in the area (Changbo et al. 2015; Hou et al. 2019). Thus, CP stands out as an important strategy for China’s SD, which should continue to invest in the replacement of fossil fuels, R&D of clean technologies, and encourage public-private cooperation in developing solutions to the country’s environmental problems (Soylu et al. 2021).
United States of America
The United States of America (USA) is the country with the third-largest H-index in CP theme (H-index = 10). The USA’s high industrialization has made it one of the most polluting countries in the world (US EPA 2020a). Thus, the importance of addressing environmental impacts and preventing pollution generation was realized even before the CP concept emerged. Between the 1970s and 1990s, the American government enacted several environmental laws regulating the main practices that were causing the pollution of the country’s soil, air, and water (Miller et al. 2008). However, many of them still had an end-of-pipe approach, being directed to pollution control, treatment, and disposal only after it was generated (Burnett 1998; Miller et al. 2008).
The US Environmental Protection Agency (EPA) is the primary government agency responsible for protecting the American environment. Since its establishment in 1970, the agency has been developing environmental laws, overseeing its enforcement and encouraging research into sustainable solutions to the country’s environmental problems (US EPA 2020b).
American private companies played an important role in developing strategies focused on pollution prevention in the USA, which subsequently became the basis of the country’s environmental policies. The large multinational 3M emerged with the Pollution Prevention Pays (3P) strategy in 1975, which was widely adopted by several other companies.
3P works to prevent pollution by reducing waste at source, adopting new technologies, changing processes and raw materials, and establishing an incentive program for employees to suggest and implement solutions to reduce the companies’ environmental impacts. At 3P, improvements should ensure financial return by reducing waste and pollution control costs (Miller et al. 2008; Ochsner et al. 1995).
These pollution prevention initiatives have been titled in many ways in the USA, including waste minimization, waste reduction, cleaner production, and pollution prevention (P2), the most widely adopted in the country (Miller et al. 2008). In 1990, the EPA introduced the Pollution Prevention Act, officializing pollution prevention at the source (P2) as the official strategy of the US government as opposed to end-of-pipe approaches. Strategies were defined focusing on industry, government, and public attention on reducing the amount of pollution through cost-effective changes in production, operation, and raw material use (Harrington 2013; US EPA 2020c).
Thus, the USA has achieved several advances in reducing the pollution generated by its companies (Shapiro and Walker 2018). Between 1991 and 2012, the EPA conducted about 370,000 pollution prevention projects through the Toxic Release Inventory (TRI) Program in several American industries. It is estimated that each of these projects reduced the emission of chemicals from 9 to 16% per year, totaling a prevention of generation of 5 to 6.35 billion kilos in chemical waste (Ranson et al. 2015).
In the academic-scientific area, Prof. Dr. Donald Huisingh stands out as the second author with the highest H-index among the 10 most cited authors in this area. He has extensive experience with CP. During his life, he has supported the CP practice implementation in more than 300 organizations and founded JCP, being currently the journal Editor-in-Chief Emeritus (Elsevier 2020a).
The JCP is one of the main periodicals in the CP area. Founded in 1993, it acts as a platform for theoretical and practical discussion on CP practice advances and applications. Among the 30 most cited articles in the period studied and available at Scopus, 29 were published in this periodical, indicating his high relevance (Elsevier 2020b).
Five of the 30 papers analyzed have American authors’ participation. Khalili et al. (2015) proposed the application of a methodology to leaders of higher education could assess the necessity of creating training programs to develop the human capital needed to support SD, infusing CP concepts and theories at academic programs. The proposed methodology was formulated to utilize expert judgment to assess the importance of a matrix of CP—SD indicators needed for the design of CP-infused academic programs in teaching and research. Almeida et al. (2015, 2017)) identified CP strategies proposed on the published articles in the 4th and 5th International Workshop Advances in Cleaner Production, respectively, to help companies, government, and society to speed up to SD. The strategies are focused on sustainability strategies, raw material replacement, renewable energy, technological developments, and product and policy changes. Yilmaz et al. (2015) analyzed eleven best available techniques (BATs) of cleaner production for iron casting process, using a life-cycle approach (LCA). The BATs analyzed decreased overall environmental impact of casting by 60–90%. Finally, Ortolano et al. (2014) evaluated the dissemination of cleaner production in Pakistan’s industrial sector by assessing the performance of two of Pakistan’s CP centers and the survey of 80 leather tannery and textile processing firms.
Among the 10 research institutes that have published the most cited articles in the CP area, 2 are American: University of Tennessee (UT) and Illinois Institute of Technology (IIT). UT has important research centers, with emphasis on CP as the Institute of Secure and Sustainable Environment (ISSE). This institute was established to promote the development of policies, technologies, and educational programs in response to environmental issues faced by the world (ISSE 2020).
The second institute is IIT. Its studies on CP were conducted by the Stuart School of Business between 2014 and January 2020. IIT developed the pathways to CP in the Americas project, where partnerships were made among research institutes and companies from 8 countries of the American continent (the USA, Costa Rica, the Dominican Republic, El Salvador, Guatemala, Honduras, Nicaragua, Peru). The objective of the project was to promote and facilitate the adoption of sustainable practices in these countries (Ashton et al. 2017; McPherson et al. 2016).
The most important actions were the strengthening of CP practice teaching in higher education institutions, the sensitization of micro, small, and medium enterprises regarding the CP benefits, the conduction of CP implementation in the project’s partner companies, and the creation of a collaboration forum for the exchange of knowledge among these countries (Ashton et al. 2017; McPherson et al. 2016).
Figure 5 shows that the USA is the second country with most CT priority patents registered between 2000 and 2020. Thus, the public and private initiatives on pollution prevention practices combined with the initiatives from American research centers have made the USA a powerhouse in the development of CT. The latest patents filed under cleaner production were “Stimulation of geothermal wells and removal of silica-based deposit” and “Virtual landfill terminal”.
The patent “Stimulation of geothermal wells and removal of silica-based deposit” is intended for geothermal plants, i.e., power plants that produce energy using heat from the Earth’s interior. Despite being considered a clean energy source, this energy matrix often suffers in maintaining its reservoirs active over time. The most recurrent solutions to avoid interruptions in the operation of these plants are the use of explosives in the wells of the geothermal plant and mechanisms that produce water at high pressure. However, these procedures are dangerous, waste resources—such as water—and require the shutdown of the plants while these interventions are being carried out. To solve this problem, the inventors aim to include a silica-based deposit in the good casing, allowing the alternate injection of an acidic and a caustic composition, artificially producing steam in the water at times of need. In this way, the continuity of energy production is stimulated, using a safer, less polluting mechanism, and without the need for a temporary shutdown of the plant while the necessary repairs are made (Bluemle et al. 2020).
The “Virtual Landfill Terminal” patent is a method that allows the treatment and disposal of solid waste in a single facility. Solid waste is separated into biomass and plastic recyclables. The biomass is transformed into syngas by means of a gasifier. The plastics are processed in this facility, and turned into naphtha, diesel, and/or lubricants. The heat from the biomass and plastics is also captured and used to generate electricity. This structure allows for energy production with less environmental impact, and a significant decrease in oil as a feedstock (Kirkendoll and Tuck 2021).
Therefore, pollution prevention in the country is promoted by national, state, and local programs, private initiatives such as 3P, and scientific research from research institutes, which also have important roles on the development of CP practices in the USA (Miller et al. 2008).
Malaysia
Malaysia is the fourth country with the largest H-index on the subject (H-index = 8). Its economy was based on the export of commodities until the 1980s when the country began its industrialization (Auyong and Chin 2019; Rahim and Raman 2015; The World Bank 2019). Malaysia’s average GDP growth was 9% per year between 1998 and 1996 due to policies to encourage domestic industry, infrastructure, and urban expansion (Muyibi et al. 2008; Rahim and Raman 2015; The World Bank 2020).
The growth of Malaysia’s manufacturing sector has exposed the country to several environmental problems. Some studies show the depletion of fishing reserves, air pollution, water pollution, soil pollution, and industrial waste generation as the main challenges faced in the country (Abdullah 1995; Afroz et al. 2003; Muyibi et al. 2008; Poon et al. 2016; Rani et al. 2018).
Since the identification of these environmental problems, the government took initiatives to combat them. Early in the industrialization of Malaysia, its government enacted the Environmental Quality Act (Malaysia, 1974), marking the beginning of the country’s efforts in their enterprises’ environmental management. This act regulates measures to prevent, reduce, and control pollution in the industry (Abdullah 1995).
A few years later, in 1976, the Department of the Environment (DOE) was created under the Ministry of Natural Resources and the Environment. DOE is responsible for ensuring SD and maintaining a safe, clean, and healthy environment. It supports and oversees sectors of society in adopting sustainable measures (Abdullah 1995; DOE 2020; Yusup et al. 2014).
The DOE adopted CP in 2002 as a pollution prevention practice to be employed in Malaysian industries. The first CP measures and projects were directed to small and medium enterprises since they are most of the country’s industrial sector (Rahim and Raman 2015; Yusup et al. 2014).
Researchers from the University of Technology of Malaysia were selected to develop a national program for the CP practice promotion in the country. The studies resulted in the “Cleaner Production Blueprint for Malaysia,” which was published in 2007. This document outlines the national plan for the CP promotion in Malaysia, defining strategies for the CP concept and practice development and the dissemination of CTs among the country’s companies (DOE 2007; Yusup et al. 2014).
The main actions proposed in this plan include the dissemination of information and training of professionals to support the CP practice adoption, guidelines for training, conducting audits, tax incentives to companies, and incentive to clean technology research centers. Also, in 2007, the DOE published the “Cleaner Production Audit Guidelines” standardizing and promoting CP audits in the country (Yusup et al. 2014).
A few years later, in 2009, the Ministry of Energy, Green Technology, and Water enacted a new national policy, the National Green Technology Policy. It defines initiatives to encourage the use of CTs focused on four aspects: energy, environmental, economic, and social. In continuity with this policy, the Green Technology Master Plan Malaysia was launched in 2017, defining objectives to be achieved by 2030 in the dimensions of energy, manufacturing, transportation, civil construction, waste, and water, aiming at the sustainable use of natural resources (Ministry of Energy Green Technology and Water 2017; Yusup et al. 2014).
Therefore, the universities of Malaysia have been conducting outstanding international research in the CP area. The articles generated by these studies were cited 264 times. Two Malaysian researchers are among the ten most cited authors in CP theme: Prof. Dr. Lai Fatt Chuah and Prof. Dr. Suzana Yusup.
Prof. Lai Fatt Chuah is affiliated with Petronas University of Technology (UTP), and his studies aim at the development and application of new raw materials and production processes for biodiesel manufacturing. Prof. Dr. Suzana Yusup is a chemical engineer also affiliated to UTP. She founded the Biomass Processing Laboratory and studies about green technologies at the university, developing new biomass use processes and clean materials.
Three of the 30 papers analyzed have Malaysian authors’ participation. Hayyan et al. (2014) developed a methodology to convert acidic crude palm oil (ACPO) to fatty acid methyl esters (FAME), raw materials used to produce biodiesel. This technology can reduce the total cost of biodiesel production, helping this industry and catalyzing the achievement of green energy goals in Malaysia. Bokhari et al. (2016) developed a cleaner production process of rubber seed oil methyl ester using hydrodynamic cavitation. This technology is a viable way to offset fossil diesel usage, reducing energy consumption during biodiesel production. Finally, Chuah et al. (2016) developed a cleaner production process of methyl ester using waste cooking oil. Methyl ester is biodegradable, renewable, and nontoxic, produces less sulfur oxides emissions and greenhouse gases, and can be used as an alternative fuel to replace petroleum diesel, reducing the environmental impacts.
Regarding patents, the last two registered in cleaner production were “Brush cleaning elements and method of manufacturing the same” and “Systems to remove non-aromatic compounds for the production of para-xylene”. The patent “Brush cleaning elements and method of its manufacture” is a method of including adhesive tapes inside industrial vacuum cleaners. With these tapes, the vacuum cleaner provides better conditions of humidity and resistance to debris, preserving the internal structure of the equipment and consequently increasing its useful life. This method reduces material waste and improves vacuum cleaner efficiency (Lee 2021). The patent “Systems to remove non-aromatic compounds for the production of para-xylene” is a system that removes non-aromatic compounds from xylene by isomerization. A clay container is used in this system, separating the non-aromatic compounds from the xylenes into different compartments. In this way, the separation between the elements is cleaner, eliminating the need to include toxic substances to separate the elements (Abichandani et al. 2021).
Therefore, despite being a country with recent industrialization, Malaysia has achieved strong economic growth based on the use of its natural resources to leverage its manufacturing. Thus, to ensure lasting success, the country’s government realized that SD should be one of its goals. The policies adopted to promote CP have made Malaysia an example that public policies focused on SD are essential to promote the country’s green growth (Yusup et al. 2014).
CP scientific development opportunities and challenges
In this topic are the analyses of scientific opportunities and challenges for CP development. The scientific opportunities were identified in the 30 most cited articles and grouped according to the similarities between them, originating the clusters presented in Table 2.
CT and CP practices have been disseminated diffusely and slowly in many countries, despite their many proven benefits (Bonilla et al. 2010). Therefore, it is necessary to encourage the development of sustainable actions and to study the factors that motivate companies to adopt them (cluster 1).
The industrial companies’ environmental performance should be measured to facilitate the identification of improvement opportunities. To this end, the formation of partnerships between them and universities is encouraged. According to Almeida et al. (2017), this facilitates the design and practical application of tools and technologies developed by researchers.
The use of technologies to control and minimize pollution in manufacturing processes enables the reduction of their environmental impacts and generates a competitive advantage for companies (Khorasanizadeh et al. 2016). However, Yong et al. (2016) state that some pollution control equipment is expensive, complex, and does not have an adequate design for implementation, making its use difficult. Thus, the importance of developing new technologies, processes, and clean products suitable for the real needs of companies is highlighted.
Severo et al. (2017) say there is a correlation between the size of companies and the ease of CP implementation. Usually, medium and large companies are more able to invest financial resources in R&D of clean processes, sustainable products, and new CP methodologies and tools. However, the small companies present greater difficulties for this type of initiative.
Therefore, it is possible to observe research opportunities in the area of new technology development (cluster 2) encouraging the implementation of CP actions in companies of several sizes (cluster 1). It is necessary to adapt these new technologies to the various sectors’ production processes to eliminate, minimize, or reuse the waste generated (Bokhari et al. 2016).
Still aiming at more efficient processes and more recyclable, reusable, and degradable products, research opportunities for developing sustainable products were identified (cluster 3). The substitution of raw materials and improvement of production processes (Chuah et al. 2016; Deutz et al. 2018; Hayyan et al. 2014), the change of material’s chemical properties (Dahunsi et al. 2017; Mia et al. 2018), and use of more efficient production methods (Bokhari et al. 2016) are important initiatives that can be employed in the CP development in industries and can be developed from scientific research.
Another opportunity is to develop new tools and methods that would enable CP development approaches adapted to different countries and business sector realities (cluster 4) (Henriques and Catarino 2015; Jia et al. 2014). Obtaining ISO 14001 certification is one way to foster CP development actions (De Oliveira et al. 2016). ISO 14001, for example, promotes an environmentally friendly culture in companies by incorporating concern with environmental impacts into the day-to-day lives of employees and assisting in the allocation of resources for environmental management decision-making, facilitating the CP action’s adoption.
The development of studies on the promotion of clean energy matrices and the use of renewable energy in companies as a scientific opportunity (cluster 5) was also identified. Sáez-Martínez et al. (2016) state that the development of more promising techniques to extract the maximum from the available energy in organic matter, the substitution of fossil fuel by renewable, and the optimization of clean energy matrices are important improvements that allow minimizing the costs of energy use and facilitate the adoption of renewable energy. Therefore, it is essential to develop new strategies to encourage the use of alternative energy sources that have fewer negative impacts on the environment (Scarazzato et al. 2017).
There is also a need to identify the difficulties faced by companies during CP implementation and propose solutions for them (cluster 6) (Severo et al. 2015). This identification is possible through the analysis of the barriers faced by the various industrial sectors (Govindan et al. 2016; Ortolano et al. 2014; Silvestre and Neto 2014), analysis of environmental, economic, and social impacts from the implementation of CP actions (Severo et al. 2015), and analysis of the results of new technologies and tools used to reduce environmental impacts (Henriques and Catarino 2015).
Thus, the identification and systematization of the challenges conducted in this research aim to provide an overview of the issues that most impede the CP development. The challenges were identified in the 30 most cited articles and grouped according to their similarities and the clusters are available in Table 3.
The first challenge identified is the lack of legislation and policies to encourage CP practices in some countries. The development of a macroeconomic policy focused on the formulation of an agenda for CP adoption is essential for the SD of countries due to the important roles of governments and industries in combating social and environmental problems. However, state regulations directed to the protection of society’s social and environmental interests are still being slowly adopted; and there is a lack of articulation between the public and private sectors to adopt rules effectively appropriate to the reality of the industry. The laws of many developing countries are still guided by end-of-pipe practices, despite the positive results of pollution prevention strategies (Almeida et al. 2015; Khalili et al. 2015).
Thus, governments should strive to develop strategies focused on managing the environmental and ecological risks associated with the industrial activities of their countries (Khalili et al. 2015). Governments should organize themselves so that CP practices can be stimulated and not inhibited by bureaucracies that make their implementation difficult (Hens et al. 2018; Wesseh Jr and Lin 2015).
The second challenge identified is related to supply chain management. Efforts to disseminate sustainable and CP practices through companies’ supply chains have gained momentum (Khalili et al. 2015).
However, the complexity of supply chain management in different realities has required a high level of innovation in the search for joint reduction of material and energy waste along the chain, especially in emerging countries (Almeida et al. 2015, 2017).
Thus, initiatives such as reverse logistics and closed-loop supply chains are strategies that can be associated with CP to overcome these barriers. They encourage the planning, implementation, and control of raw material flow management practices focusing on reducing the environmental impacts of the company’s products and processes throughout their life cycles (Govindan et al. 2016; Govindan and Soleimani 2017).
The third challenge is related to organizational culture and innovation. The CP implementation requires innovations in technological, operational, managerial, and strategic aspects. However, companies have difficulties in developing an organizational culture focused on environmental innovations due to lack of support from managers, the resistance of employees to change, and lack of government regulation (Henriques and Catarino 2015; Vickers and Cordey-Hayes1999). The transition to an environmentally innovative culture requires efforts from top management, as they are responsible for identifying opportunities to implement CP practices and motivating their employees, and they should be engaged in the search for innovation (Silvestre and Neto 2014).
Framework for CP development
The framework (Table 4) proposes policies, strategies, initiatives, and research opportunities to be adopted by the triple helix entities for the CP promotion. The framework proposals were based on the critical analysis of the actions adopted by the leading countries presented in the technical-scientific scenario (the “Technical-scientific scenario” section), the scientific opportunities for CP development, and the challenges faced by companies during its implementation (the “CP scientific development opportunities and challenges” section). Those elements served as a benchmarking for the framework elaboration and were analyzed and adapted on the light of the authors’ expertise.
The actions proposed in the framework are divided into domains within each triple helix sector (government, industry, and university). The actions in the governmental sector are segmented into politics and legislation; economic; and education domains. Politics and legislation actions proposed in Table 4 are focused on regulating and driving the other spheres of triple helix to adopt CP practices. The development of laws that encourage companies to engage in solutions to their environmental impacts is a major catalyst for changes in corporate and social attitudes (Bonilla et al. 2010). Thus, the creation of a national policy based on CP and the creation of a network of support agencies for organizations at regional levels are important initiatives for the dissemination of their practices in national territories (Khalili et al. 2015; Zhang et al. 2013). Specific legislation focused on highly polluting industrial sectors is also an important incentive for companies to adopt pollution prevention strategies (Bonilla et al. 2010; Yusup et al. 2014). In this sense, the regulation of voluntary and mandatory audits allows for efficient monitoring of CP implementation (Bai et al. 2015; Hong and Li 2013).
The financial aspect is marked by the subsidy and tax incentive for CP projects with the provision of special advantages in loans for CP implementation in industrial companies (UNIDO; UNEP 2015). Pollution taxing of industries is a practice that internalizes in companies the cost of pollution generated by it, encouraging them to adopt a position of pollution prevention.
The educational aspect reinforces the responsibility of governments to invest in awareness-raising, professional training, and the development of new techniques and tools that stimulate the CP implementation. The government should invest in funding practical and theoretical research for developing CP in the country, catalyzing the creation of solutions to increase the efficiency of its industrial sector and reduce negative environmental impacts. Initiatives to structure curricula for courses on corporate sustainability and partnerships between the universities and companies for developing innovations in the CP area are also encouraged. These actions are proposed to promote and support research institutions in the development of studies and training on CP practices and the dissemination of awareness campaigns about this strategy.
The relevant actions of the academy are divided into education and research. The educational actions focus on the formation of technically trained professionals in CP practices. Like governments, institutions of higher education have an important role in this aspect by being responsible for creating the human capital necessary for developing the countries’ economy (Khalili et al. 2015). Thus, they should undertake efforts to develop the necessary training in CP domains for the successful practical applications of this strategy and to disseminate knowledge through congresses, roundtables, workshops, videos, books, and etc. (Bonilla et al. 2010).
In the research item, research fields are suggested to be explored by academic institutions and companies for developing CP knowledge. They were based on the scientific opportunities identified in this study. Efforts are suggested in the development of clean technologies, more efficient production processes, and green materials and products. The study of the difficulties faced by companies during the CP implementation and the development of strategies to overcome them are important initiatives to support the adoption of its practices. The partnerships between government, academia, and industry are fundamental because they allow the knowledge obtained to be transferred between the three spheres, making them applicable (Kimatu 2016).
Finally, the actions regarding industries are segmented into planning and management; and production. The topic of planning and management highlights the importance of the commitment of top management in adopting and encouraging CP practices. Top managers should be aware of the importance of making the necessary investments to implement CP and develop an innovative organizational culture based on SD values (Vieira and Amaral 2016; Gonçales Filho et al. 2018). Thus, the adoption of practices that facilitate the integration of CP into the company’s strategy is suggested, such as the structuring CP audits, the development of a green supply chain, and partnerships with research institutions (Ortolano et al. 2014; De Oliveira et al. 2016; de Oliveira et al. 2017).
The implementation of integrated management systems is also encouraged. Among the various standards developed by ISO, the most widely used by organizations are ISO 9001 (quality management), ISO 14001 (environmental management), ISO 45001 (occupational health and safety management), and ISO 50001 (energy management system) (Majerník et al. 2017). These standards contribute to the development of sustainability in all TBL pillars (economic, social, and environmental). In the economic pillar, ISO 9001 is a reference standard for the quality management system assisting managers in standardizing and improving products, services, and processes, reducing variability, and meeting customer needs (Ismyrlis and Moschidis 2015). In the social pillar, ISO 45001 assists managers in seeking efficiency and safety of workers. This standard assists manager in meeting the company’s legal requirements and providing salubrious occupational health and safety protection conditions for their employees (Kafel 2016).
In the environmental pillar, ISO 14001 is a benchmark standard for the environmental management system establishing environmental policies, actions, and plans. This standard helps organizations seek a balance between economic growth and reducing negative environmental impacts on society (Kafel 2016). ISO 50001 also presents requirements for companies’ efficient energy management, defining guidelines for the use of renewable energy (Nunhes et al. 2019).
Production initiatives make production processes more efficient and less polluting. Thus, practices such as replacing hazardous or polluting materials with cleaner materials, investing in more efficient processes and machines, and adopting renewable energy are suggested. Strengthening the R&D area of companies is essential to make these transformations feasible and to foster the development of clean technologies that meet the needs of their processes.
The framework also highlights the synergistic potential of joint actions and partnerships among governments, industries, and universities, which, if integrated, can leverage the CP development. The government can direct its policies to regulate and promote the use of CP practices in the industry, especially in the most polluting sectors. Government, universities, and industries can also work together to promote the development of solutions to the challenges of implementing this strategy and foster the creation of clean technology development centers; universities can build partnerships with industries to train professionals to work in environmental management and CP; industries can help funding research centers and universities to the development of clean technologies; and industries can encourage the development of research and development (R&D) sectors aimed at technology partnerships, internal organizational changes, and improvements in existing processes and products (Miotti and Sachwald 2003; Trencher et al. 2014). Thus, integrated actions between triple helix sectors can open paths to industries to move towards cleaner production processes.
Conclusion
CP is an important pollution prevention strategy used mainly in industries. Despite its benefits, several countries and commercial sectors face several challenges for its adoption. Therefore, this article proposed a development framework for CP to serve as a guide for actions to promote the strategy in the three spheres of the triple helix, reaching the objective of this research (Ranga and Etzkowitz 2013).
The main scientific contribution of this work was to articulate CP theory with the CP technical-scientific scenario identifying the benefits and challenges of its applications. Thus, this work contributes to the CP study area and encourages studies and research in this line of research minimizing its current challenges.
The main applied contribution of this work was to develop a framework for governments, industries, and scientific academia, based on the analysis of the CP technical-scientific scenario, CP implementation opportunities, and difficulties. It is expected that with the initiatives proposed in the framework, CP’s practices will be easier to implement, reducing pollution generation in the industry, increasing the efficiency of its processes, and aligning countries and societies to sustainable development.
Thus, the main novelty of this work is the proposal of an innovative and unprecedented framework with initiatives based on CP good practices and development opportunities identified from the analysis of the technical-scientific scenario and literature. The framework serves as a guide for the main institutions responsible for solving global environmental problems to reduce barriers to the expansion of this strategy.
However, CP practices and their difficulties may vary according to the country and the industrial sector studied (Ortolano et al. 2014). Thus, the limitation of this study is related to the criteria chosen for the country selection and initiatives of prominence in the CP area, which if changed, could present results that complement the framework proposed.
The selection criteria adopted for the countries prioritized their academic performance; therefore, Brazil, China, the USA, and Malaysia stand out in the development of scientific knowledge on the subject. However, while the USA (3rd position) and China (14th position) are on the top of the Global Innovation Index (GII) of 2020, Brazil (64th position) and Malaysia (33rd position) still need to improve innovation creation, fostering CP practical applications and investing in the development of technologies by their universities, research centers, and companies (Cornell University, INSEAD, and WIPO 2020). Furthermore, important countries in industrial technical development such as India, Pakistan, South Korea, Colombia, the UK, and Hungary have not been considered in the studies.
Thus, the achievement of studies in other contexts is suggested, using new combinations of criteria and metrics to identify good practices and needs of different countries and sectors. Additional studies are also suggested in each sphere of the triple helix, to encourage closer relations between them (industry-academia-government), creating national/regional cells for promoting innovations in this area. Future studies that consider cleaner production applications in industrial sectors, such as textiles, metallurgy, food, and technology, among others, are encouraged. Therefore, it is possible to mobilize a set of tools that enhance the sustainable development of various economic segments, attending to their specificity.
Availability of data and material (data transparency)
Data sharing not applicable. No new data were created or analyzed in this study. Data sharing is not applicable to this article. All data generated or analyzed during this study are included in this published article (and its supplementary information files).
Code availability (software application or custom code)
Not applicable.
References
Abdullah AR (1995) Environmental pollution in Malaysia: trends and prospects. Trends Anal Chem 14:191–198. https://doi.org/10.1016/0165-9936(95)91369-4
Abichandani J, Cheng W, Minhas B, Tinger R, Van Nuland M, Wang C-J. (2021) Non-aromatic compound removal systems for para-xylene production. (Patent: WO2021029981A1). Espacenet. bit.ly/3gmWSwf. Accessed 21 Aug 2021
ACPN (2020) Advances in cleaner production network | boosting knowledge exchange seeking for sustainability. http://www.advancesincleanerproduction.net/network/. Accessed 2 Apr 2020
Adebayo TS, Adedoyin FF, Kirikkaleli D (2021a) Toward a sustainable environment: nexus between consumption-based carbon emissions, economic growth, renewable energy and technological innovation in Brazil. Environ Sci Pollut Res 2021:1–11. https://doi.org/10.1007/S11356-021-14425-0
Adebayo TS, Awosusi AA, Odugbesan JA, Akinsola GD, Wong WK, Rjoub H (2021b) Sustainability of energy-induced growth nexus in Brazil: do carbon emissions and urbanization matter? Sustain 2021 13:4371. https://doi.org/10.3390/SU13084371 Accessed 21 Aug 2021
Afroz R, Hassan MN, Ibrahim NA (2003) Review of air pollution an health impacts in Malaysia. Environ Res 92:71–77. https://doi.org/10.1016/s0013-9351(02)00059-2
Ajadi T, Boyle R, Strahan D et al (2019) Global trends in renewable energy investment, Bloomberg New Energy Finance.
Almeida CMVB, Agostinho F, Giannetti BF, Huisingh D (2015) Integrating cleaner production into sustainability strategies: an introduction to this special volume. J Clean Prod 96:1–9. https://doi.org/10.1016/j.jclepro.2014.11.083
Almeida CMVB, Agostinho F, Huisingh D, Giannetti BF (2017) Cleaner Production towards a sustainable transition. J Clean Prod 142:1–7. https://doi.org/10.1016/j.jclepro.2016.10.094
Aparecido D, Silva L, Delai I et al (2013) Quality tools applied to Cleaner Production programs: a fi rst approach toward a new methodology. J Clean Prod 47:174–187. https://doi.org/10.1016/j.jclepro.2012.10.026
Ashton WS, Hurtado-Martin M, Anid NM, Khalili NR, Panero MA, McPherson S (2017) Pathways to cleaner production in the Americas I: bridging industry-academia gaps in the transition to sustainability. J Clean Prod 142:432–444. https://doi.org/10.1016/j.jclepro.2016.03.116
Auyong HN, Chin YH (2019) Cleaner production and sustainability: stakeholder pressure and the adoption of pollution prevention measures of industrial hazardous waste in Malaysia. IOP Conf Ser Earth Environ Sci 268:012027. https://doi.org/10.1088/1755-1315/268/1/012027
Bai Y, Yin J, Yuan Y, Guo Y, Song D (2015) An innovative system for promoting cleaner production: mandatory cleaner production audits in China. J Clean Prod 108:883–890. https://doi.org/10.1016/j.jclepro.2015.07.107
Baptista VTR, Lôbo RP, Souza LJC et. al. (2020). Possibilities for new space hubs in Brazil. In Proceedings of the International Astronautical Congress, IAC (Vol. 2020-October). International Astronautical Federation, IAF.
Bluemle M; Carey WS; Hewson P; Lynch MN; Muller L; Slijp P (2020). Geothermal well stimulation and silca based deposit removal (Patent US2021222517A1). Espacenet. bit.ly/3ycQQED. Accessed 21 Aug 2021
Bokhari A, Chuah LF, Yusup S, Klemeš JJ, Akbar MM, Kamil RNM (2016) Cleaner production of rubber seed oil methyl ester using a hydrodynamic cavitation: optimisation and parametric study. J Clean Prod 136:31–41. https://doi.org/10.1016/j.jclepro.2016.04.091
Bonilla SH, Almeida CMVB, Giannetti BF, Huisingh D (2010) The roles of cleaner production in the sustainable development of modern societies: an introduction to this special issue. J Clean Prod 18:1–5. https://doi.org/10.1016/j.jclepro.2009.09.001
Brazil (2006) MMA incentiva criação de fóruns estaduais de Produção Mais Limpa. https://www.mma.gov.br/informma/item/3058-mma-incentiva-criacao-de-foruns-estaduais-de-producao-mais-limpa.html. Accessed 4 Dec 2019
Brazil (2011) Plano de Ação para Produção e Consumo Sustentáveis – PPCS. https://antigo.mma.gov.br/responsabilidade-socioambiental/producao-e-consumo-sustentavel/plano-nacional.html. Accessed 4 Dec 2019
Brazil (2014) Plano de ação para produção e consumo sustentáveis - PPCS: Relatório do primeiro ciclo de implementação. Brasília. https://antigo.mma.gov.br/responsabilidade-socioambiental/producao-e-consumo-sustentavel/plano-nacional.html. Accessed 4 Dec 2019
Burnett ML (1998) The pollution prevention act of 1990: a policy whose time has come or symbolic legislation? Environ Manag 22:213–224. https://doi.org/10.1007/s002679900098
Campos TLR, da Silva FF, de Oliveira KB, de Oliveira OJ (2020) Maturity grid to evaluate and improve environmental management in industrial companies. Clean Techn Environ Policy 22:1485–1497. https://doi.org/10.1007/s10098-020-01887-y
Changbo Z, Zi L, Jingjun L, et al (2015) Analysis on the status for cleaner production in China. Proc - 2015 5th Int Work Adv Clean Prod
Chuah LF, Yusup S, Abd Aziz AR, Bokhari A, Abdullah MZ (2016) Cleaner production of methyl ester using waste cooking oil derived from palm olein using a hydrodynamic cavitation reactor. J Clean Prod 112:4505–4514. https://doi.org/10.1016/j.jclepro.2015.06.112
Cleaner Production Promotion Law (2002) Cleaner Production Promotion Law. http://extwprlegs1.fao.org/docs/pdf/chn46926E.pdf. Accessed 04 Jan 2021
CNTL, SENAI, UNIDO, UNEP (2003) Five Phases of Cleaner Production Techniques Implementation/Cinco Fases da Implantação de Técnicas de Produção mais Limpa. Porto Alegre. https://www.senairs.org.br/sites/default/files/documents/manual_cinco_fases_da_produthoo_mais_limpa.pdf. Accessed 4 Dec 2019
Cornell University, INSEAD, and WIPO (2020). The Global Innovation Index 2020: who will finance innovation? Ithaca, Fontainebleau, and Geneva. https://www.globalinnovationindex.org/Home. Accessed 21 Aug 2021
Costa ACF, de Mello Santos VH, de Oliveira OJ (2021) Towards the revolution and democratization of education: a framework to overcome challenges and explore opportunities through Industry 4.0. Inform Educ. https://doi.org/10.15388/infedu.2022.01
da Motta Reis JS, Costa ACF, Espuny M et al (2020) Education 4.0: gaps research between school formation and technological development. 17th International Conference on Information Technology–New Generations (ITNG 2020). Advances in Intelligent Systems and Computing, v. 1134. Springer, Cham. https://doi.org/10.1007/978-3-030-43020-7_55
Da Silva AG, Januario MJ (2021). Production of ceramic proppant from iron ore and/or waste rock from its exploitation and/or tailings from its beneficiation with an agglomeration of fine and ultrafine particles. (BR Patent No. AU2019275674A1) BR National Institute of Industrial Property (INPI). bit.ly/2UFod52. Accessed 21 Aug 2021
Dahunsi SO, Oranusi S, Efeovbokhan VE (2017) Cleaner energy for cleaner production: modeling and optimization of biogas generation from Carica papayas (Pawpaw) fruit peels. J Clean Prod 156:19–29. https://doi.org/10.1016/j.jclepro.2017.04.042
De Oliveira JA, Oliveira OJ, Ometto AR et al (2016) Environmental Management System ISO 14001 factors for promoting the adoption of Cleaner Production practices. J Clean Prod 133:1384–1394. https://doi.org/10.1016/j.jclepro.2016.06.013
de Oliveira JA, Silva DAL, Guardia M, do Nascimento Gambi L, de Oliveira OJ, Ometto AR (2017) How can Cleaner Production practices contribute to meet ISO 14001 requirements? Critical analysis from a survey with industrial companies. Clean Techn Environ Policy 19:1761–1774. https://doi.org/10.1007/s10098-017-1363-8
Deutz S, Bongartz D, Heuser B, Kätelhön A, Schulze Langenhorst L, Omari A, Walters M, Klankermayer J, Leitner W, Mitsos A, Pischinger S, Bardow A (2018) Cleaner production of cleaner fuels: wind-to-wheel-environmental assessment of CO2-based oxymethylene ether as a drop-in fuel. Energy Environ Sci 11:331–343. https://doi.org/10.1039/c7ee01657c
Dobes V (2013) New tool for promotion of energy management and cleaner production on no cure, no pay basis. J Clean Prod 39:255–264. https://doi.org/10.1016/j.jclepro.2012.08.007
DOE (2007) Cleaner production blueprint for Malaysia. https://cp.doe.gov.my/cpvc/wp-content/uploads/2012/05/Cleaner-Production-Blueprint-For-Malaysia.pdf. Accessed 27 Mar 2020
DOE (2020) Director General’s Message | Department of Environment. In: Dep. Environ. https://www.doe.gov.my/portalv1/en/tentang-jas/pengenalan/perutusan-ketua-pengarah. Accessed 27 Mar 2020
Dong L, Tong X, Li X, Zhou J, Wang S, Liu B (2019) Some developments and new insights of environmental problems and deep mining strategy for cleaner production in mines. J Clean Prod 210:1562–1578. https://doi.org/10.1016/j.jclepro.2018.10.291
Elo S, Forman J, Damschroder L (2007) Qualitative content analysis. Adv Bioeth 11:39–62. https://doi.org/10.1016/S1479-3709(07)11003-7
Elsevier (2020a) Don Huisingh - Founder and Editor-in-Chief Emeritus. J Clean Prod. https://www.journals.elsevier.com/journal-of-cleaner-production/editorial-board/don-huisingh. Accessed 20 July 2020.
Elsevier (2020b). Journal of Cleaner Production - Elsevier. https://www.journals.elsevier.com/journal-of-cleaner-production Accessed 20 July 2020.
Espuny M, Faria Neto A, da Motta Reis JS, dos Santos Neto ST, Nunhes TV, de Oliveira OJ (2021) Building new paths for responsible solid waste management. Environ Monit Assess 193:442. https://doi.org/10.1007/s10661-021-09173-0
Etzkowitz, H (2008) The Triple Helix: University-Industry-Government Innovation in Action (1st ed.). Routledge. https://doi.org/10.4324/9780203929605
Faé Gomes GM, César A, Vilela F et al (2013) Aspects for a cleaner production approach for coal and biomass use as a decentralized energy source in southern Brazil. J Clean Prod 47:85–95. https://doi.org/10.1016/j.jclepro.2012.09.037
FAPESP (2020) Biagio Fernando Giannetti - Biblioteca Virtual da FAPESP. https://bv.fapesp.br/pt/pesquisador/2244/biagio-fernando-giannetti/. Accessed 27 Mar 2020
Fei, Z.; Feng, Z.; Wu, J.; Yi, Z.; Zhou, S. (2019). Notification method for refrigerator, apparatus, and refrigerator (Patent CN113124631A). Espacenet. bit.ly/3mtdypt. Accessed 21 Aug 2021
Fréon P, Durand H, Avadí A, Huaranca S, Orozco Moreyra R (2017) Life cycle assessment of three Peruvian fishmeal plants: toward a cleaner production. J Clean Prod 145:50–63. https://doi.org/10.1016/j.jclepro.2017.01.036
Gonçales Filho M, Nunhes TV, Barbosa LCFM, de Campos FC, de Oliveira OJ (2018) Opportunities and challenges for the use of cleaner production to reduce water consumption in Brazilian sugar-energy plants. J Clean Prod 186:353–363. https://doi.org/10.1016/j.jclepro.2018.03.114
González R (2005) Analysing the factors influencing clean technology adoption: a study of the Spanish pulp and paper industry. Bus Strateg Environ 37:20–37. https://doi.org/10.1002/bse.426
Govindan K, Soleimani H (2017) A review of reverse logistics and closed-loop supply chains: a Journal of Cleaner Production focus. J Clean Prod 142:371–384. https://doi.org/10.1016/j.jclepro.2016.03.126
Govindan K, Shankar KM, Kannan D (2016) Application of fuzzy analytic network process for barrier evaluation in automotive parts remanufacturing towards cleaner production e a study in an Indian scenario. J Clean Prod 114:199–213. https://doi.org/10.1016/j.jclepro.2015.06.092
Hall BH, Helmers C (2013) Innovation and diffusion of clean/green technology: can patent commons help? J Environ Econ Manag 66:33–51. https://doi.org/10.1016/j.jeem.2012.12.008
Harrington DR (2013) Effectiveness of state pollution prevention programs and policies. Contemp Econ Policy 31:255–278. https://doi.org/10.1111/j.1465-7287.2011.00312.x
Hayyan A, Ali M, Hayyan M et al (2014) A new processing route for cleaner production of biodiesel fuel using a choline chloride based deep eutectic solvent. J Clean Prod 65:246–251. https://doi.org/10.1016/j.jclepro.2013.08.031
Henriques J, Catarino J (2015) Sustainable Value and Cleaner Production e research and application in 19 Portuguese SME. J Clean Prod 96:379–386. https://doi.org/10.1016/j.jclepro.2014.02.030
Hens L, Block C, Cabello-Eras JJ, Sagastume-Gutierez A, Garcia-Lorenzo D, Chamorro C, Herrera Mendoza K, Haeseldonckx D, Vandecasteele C (2018) On the evolution of “Cleaner Production” as a concept and a practice. J Clean Prod 172:3323–3333. https://doi.org/10.1016/j.jclepro.2017.11.082
Hirsch JE (2005) An index to quantify an individual’s scientific research output. Proc Natl Acad Sci U S A 102:16569–16572. https://doi.org/10.1073/pnas.0507655102
Hong J, Li X (2013) Speeding up cleaner production in China through the improvement of cleaner production audit. J Clean Prod 40:129–135. https://doi.org/10.1016/j.jclepro.2012.09.024
Hong Y; Li H; Wu Y (2021) Improved coated label cloth and manufacturing method therefor (Patent WO2021134176A1). Espacenet. bit.ly/3mzuTgu. Accessed 21 Aug 2021
Hou H, Shao S, Zhang Y, Sun D, Yang Q, Qin C, Sun X (2019) Cleaner Production assessment for sea cucumber aquaculture: methodology and case studies in Dalian, China. Clean Techn Environ Policy 21:1751–1763. https://doi.org/10.1007/s10098-019-01746-5
Hoyos-Martínez PL, Merle J, Labidi J et al (2019) Tannis extraction: a key point for their valorization and cleaner production. J Clean Prod 206:1138–1155. https://doi.org/10.1016/j.jclepro.2018.09.243
Hsieh HF, Shannon SE (2005) Three approaches to qualitative content analysis. Qual Health Res 15:1277–1288. https://doi.org/10.1177/1049732305276687
Huang Y, Luo J, Xia B (2013) Application of cleaner production as an important sustainable strategy in the ceramic tile plant e a case study in Guangzhou, China. J Clean Prod 43:113–121. https://doi.org/10.1016/j.jclepro.2012.12.013
Ismyrlis V, Moschidis O (2015) The effects of ISO 9001 certification on the performance of Greek companies. TQM J 27(1):150–162. https://doi.org/10.1108/TQM-07-2013-0091
ISSE, (2020). Institute for a Secure & Sustainable Environment | The University of Tennessee, Knoxville. http://isse.utk.edu/index.html Accessed 05 July 2020.
Jakrawatana N, Pingmuangleka P, Gheewala SH (2016) Material flow management and cleaner production of cassava processing for future food, feed and fuel in Thailand. J Clean Prod 134:633–641. https://doi.org/10.1016/j.jclepro.2015.06.139
Jia L, Zhang Y, Tao L, Jing H, Bao S (2014) A methodology for assessing cleaner production in the vanadium extraction industry. J Clean Prod 84:598–605. https://doi.org/10.1016/j.jclepro.2013.05.016
Jingtao JC (2019) 5 lessons from China on how to drive sustainable growth | World Economic Forum. World Econ. Forum Agenda. https://www.weforum.org/agenda/2019/08/china-sustainable-growth/ Accessed 03 July 2020.
Kafel P (2016) The place of occupational health and safety management system in the integrated management system. Int J Qual Res 10(2):311–324. https://doi.org/10.18421/IJQR10.02-05
Kan H, Chen R, Tong S (2012) Ambient air pollution, climate change, and population health in China. Environ Int 42:10–19. https://doi.org/10.1016/j.envint.2011.03.003
Khalili NR, Duecker S, Ashton W, Chavez F (2015) From cleaner production to sustainable development: the role of academia. J Clean Prod 96:30–43. https://doi.org/10.1016/j.jclepro.2014.01.099
Khorasanizadeh H, Honarpour A, Park MSA, Parkkinen J, Parthiban R (2016) Adoption factors of cleaner production technology in a developing country: energy efficient lighting in Malaysia. J Clean Prod 131:97–106. https://doi.org/10.1016/j.jclepro.2016.05.070
Kimatu JN (2016) Evolution of strategic interactions from the triple to quad helix innovation models for sustainable development in the era of globalization. J Innov Entrep 5:16. https://doi.org/10.1186/s13731-016-0044-x
Kirkendoll BR; Tuck DJ (2021). Virtual landfill terminal (Patent US2021220881A1). Espacenet. bit.ly/3jaAfwM. Accessed 21 Aug 2021
Kist LT, El Moutaqi S, Machado ÊL (2009) Cleaner production in the management of water use at a poultry slaughterhouse of Vale do Taquari, Brazil: a case study. J Clean Prod 17:1200–1205. https://doi.org/10.1016/j.jclepro.2009.04.006
Kothari CR, Garg G (2019) Research methodology: methods and techniques. New Age, New Delhi
Kubota FI, Cantorski L (2013) Identification and conception of cleaner production opportunities with the Theory of Inventive Problem Solving. J Clean Prod 47:199–210. https://doi.org/10.1016/j.jclepro.2012.07.059
Lee FY (2021). Brush cleaning elements and method of manufacturing thereof (Patent: WO2021054817A1). Espacenet. bit.ly/3sP1kZK. Accessed 21 Aug 2021
Leydesdorff L, Etzkowitz H (1996) Emergence of a Triple Helix of university—industry—government relations. Sci Public Policy 23:279–286. https://doi.org/10.1093/spp/23.5.279
Leydesdorff L, Meyer M (2006) Triple Helix indicators of knowledge-based innovation systems: introduction to the special issue. Res Policy 35:1441–1449. https://doi.org/10.1016/j.respol.2006.09.016
Li Z, Ma Z, van der Kuijp TJ, Yuan Z, Huang L (2014) A review of soil heavy metal pollution from mines in China: pollution and health risk assessment. Sci Total Environ 468–469:843–853. https://doi.org/10.1016/j.scitotenv.2013.08.090
Liu J, Diamond J (2005) China’s environment in a globalizing world. Nature 435:1179–1186. https://doi.org/10.1038/4351179a
Long JJ, Xu HM, Cui CL, Wei XC, Chen F, Cheng AK (2014) A novel plant for fabric rope dyeing in supercritical carbon dioxide and its cleaner production. J Clean Prod 65:574–582. https://doi.org/10.1016/j.jclepro.2013.08.008
Lu Y, Song S, Wang R, Liu Z, Meng J, Sweetman AJ, Jenkins A, Ferrier RC, Li H, Luo W, Wang T (2015) Impacts of soil and water pollution on food safety and health risks in China. Environ Int 77:5–15. https://doi.org/10.1016/j.envint.2014.12.010
Majerník M et al (2017) Design of integrated management systems according to the revised iso standards. Pol J Manag Stud (15, 1):135–143. https://doi.org/10.17512/pjms.2017.15.1.13
Malaysia (1974) Environmental Quality Act. https://www.env.go.jp/en/recycle/asian_net/Country_Information/Law_N_Regulation/Malaysia/Malaysia_mal13278.pdf. Accessed 17 Oct 2021.
McPherson S, Anid NM, Ashton WS, Hurtado-Martín M, Khalili N, Panero M (2016) Pathways to Cleaner Production in the Americas II: application of a competency model to experiential learnings for sustainability education. J Clean Prod 135:907–918. https://doi.org/10.1016/j.jclepro.2016.06.138
Mendes JC, Vasconcelos REF, Peixoto RAF (2018). Concreto Termo Isolante. (BR Patent No. 102018010193). BR National Institute of Industrial Property (INPI). https://www.lens.org/lens/patent/143-767-955-797-788/frontpage. Accessed 21 Aug 2021
Mia M, Gupta MK, Singh G, Królczyk G, Pimenov DY (2018) An approach to cleaner production for machining hardened steel using different cooling-lubrication conditions. J Clean Prod 187:1069–1081. https://doi.org/10.1016/j.jclepro.2018.03.279
Miller G, Burke J, McComas C, Dick K (2008) Advancing pollution prevention and cleaner production - USA’s contribution. J Clean Prod 16:665–672. https://doi.org/10.1016/j.jclepro.2007.02.2013
Ministry of Energy Green Technology and Water (2017) Green Technology Master Plan Malaysia 2017 - 2030. https://policy.asiapacificenergy.org/node/3437. Accessed 21 Aug 2021
Miotti L, Sachwald F (2003) Co-operative R&D: why and with whom? An integrated framework of analysis. Res Policy 32:1481–1499. https://doi.org/10.1016/S0048-7333(02)00159-2
Mongeon P, Paul-Hus A (2016) The journal coverage of Web of Science and Scopus: a comparative analysis. Scientometrics 106:213–228. https://doi.org/10.1007/s11192-015-1765-5
Muyibi SA, Ambali AR, Eissa GS (2008) The impact of economic development on water pollution: trends and policy actions in Malaysia. Water Resour Manag 22:485–508. https://doi.org/10.1007/s11269-007-9174-z
Nemet A, Varbanov PS, Klemeš JJ (2016) Cleaner production, process integration and intensification. Clean Techn Environ Policy 18:2029–2035. https://doi.org/10.1007/s10098-016-1240-x
Neto GCO, Shibao FY, Filho MG (2016) The state of research on cleaner production in Brazil. RAE Rev Adm Empres 56:547–577. https://doi.org/10.1590/S0034-759020160508
Nunhes TV, Oliveira OJ (2018) Analysis of Integrated Management Systems research: identifying core themes and trends for future studies. Total Qual Manag 0:1–23 31:1243–1265. https://doi.org/10.1080/14783363.2018.1471981
Nunhes TV, Bernardo M, Oliveira OJ (2019) Guiding principles of integrated management systems: towards unifying a starting point for researchers and practitioners. J Clean Prod 210:977–993. https://doi.org/10.1016/j.jclepro.2018.11.066
Nunhes TV, Garcia EV, Espuny M, Santos VHM, Isaksson R, de Oliveira OJ (2021) Where to go with corporate sustainability? Opening paths for sustainable businesses through the collaboration between universities, governments, and organizations. Sustainability. 13(3):1429. https://doi.org/10.3390/su13031429
Ochsner M, Chess C, Greenberg M (1995) Pollution prevention at the 3M corporation: case study insights into organizational incentives, resources and strategies. Waste Manag 15:663–672. https://doi.org/10.1016/0956-053X(96)00047-5
Orbit Intelligence. (2020) Patent list page. Available at https://www.orbit.com/?locale=en&ticket=5e66b2f5-21cd-4c95-8c78-2f69b2b49ac2&embedded=false#PatentListPage. Accessed 10 Apr. 2020
Orhan A, Adebayo TS, Genç SY, Kirikkaleli D (2021) Investigating the linkage between economic growth and environmental sustainability in India: do agriculture and trade openness matter? Sustain 2021 13:4753. https://doi.org/10.3390/SU13094753
Ortolano L, Sanchez-Triana E, Afzal J, Ali CL, Rebellón SA (2014) Cleaner production in Pakistan’s leather and textile sectors. J Clean Prod 68:121–129. https://doi.org/10.1016/j.jclepro.2014.01.015
Ozturk E, Koseoglu H, Karaboyaci M (2016) Sustainable textile production: cleaner production assessment/eco-efficiency analysis study in a textile mill. J Clean Prod 138:248–263. https://doi.org/10.1016/j.jclepro.2016.02.071
Peng H, Liu Y (2016) A comprehensive analysis of cleaner production policies in China. J Clean Prod 135:1138–1149. https://doi.org/10.1016/j.jclepro.2016.06.190
Pereira GR, Sant’Anna FSP (2012) An analysis of cleaner production in Brazil. Rev Bras Ciências Ambient 24:17–26 bit.ly/3mLFWDN
Pinkse J, Dommisse M (2009) Overcoming barriers to sustainability: an explanation of residential builders’ reluctance to adopt clean technologies. Bus Strateg Environ 18:515–527. https://doi.org/10.1002/bse.615
Pique JM, Miralles F, Berbegal-Mirabent J (2020) Application of the triple helix model in the creation and evolution of areas of innovation. In: Abu-Tair A, Lahrech A, Al Marri K, Abu-Hijleh B (eds) Proceedings of the II International Triple Helix Summit. THS 2018. Lecture Notes in Civil Engineering, vol 43. Springer, Cham. https://doi.org/10.1007/978-3-030-23898-8_17
Poon WC, Herath G, Sarker A, Masuda T, Kada R (2016) River and fish pollution in Malaysia: a green ergonomics perspective. Appl Ergon 57:80–93. https://doi.org/10.1016/j.apergo.2016.02.009
Rahim R, Raman AAA (2015) Cleaner production implementation in a fruit juice production plant. J Clean Prod 101:215–221. https://doi.org/10.1016/j.jclepro.2015.03.065
Ranga M, Etzkowitz H (2013) Triple helix systems: an analytical framework for innovation policy and practice in the knowledge society. Ind High Educ 27:237–262. https://doi.org/10.5367/ihe.2013.0165
Rani NLA, Azid A, Khalit SI et al (2018) Air pollution index trend analysis in Malaysia, 2010-15. Pol J Environ Stud 27:801–808. https://doi.org/10.15244/pjoes/75964
Ranson M, Cox B, Keenan C, Teitelbaum D (2015) The impact of pollution prevention on toxic environmental releases from U.S. manufacturing facilities. Environ Sci Technol 49:12951–12957. https://doi.org/10.1021/acs.est.5b02367
Reis JSDM, Espuny M, Nunhes TV, Sampaio NADS, Isaksson R, de Campos FC, de Oliveira OJ (2021) Striding towards sustainability: a framework to overcome challenges and explore opportunities through Industry 4.0. Sustainability 13(9):5232. https://doi.org/10.3390/su13095232
Sáez-Martínez FJ, Lefebvre G, Hernández JJ, Clark JH (2016) Drivers of sustainable cleaner production and sustainable energy options. J Clean Prod 138:1–7. https://doi.org/10.1016/j.jclepro.2016.08.094
Scarazzato T, Panossian Z, Tenório JAS, Pérez-Herranz V, Espinosa DCR (2017) A review of cleaner production in electroplating industries using electrodialysis. J Clean Prod 168:1590–1602. https://doi.org/10.1016/j.jclepro.2017.03.152
Severo EA, de Guimarães JCF, Dorion ECH, Nodari CH (2015) Cleaner production, environmental sustanability and organizational performance: an empirical study in the Brazilian Metal-Mechanic industry. J Clean Prod 96:118–125. https://doi.org/10.1016/j.jclepro.2014.06.027
Severo EA, de Guimarães JCF, Dorion ECH (2017) Cleaner production and environmental management as sustainable product innovation antecedents: a survey in Brazilian industries. J Clean Prod 142:87–97. https://doi.org/10.1016/j.jclepro.2016.06.090
Shapiro JS, Walker R (2018) Why is pollution from us manufacturing declining? The roles of environmental regulation, productivity, and trade. Am Econ Rev 108:3814–3854. https://doi.org/10.1257/aer.20151272
Shi H, Peng SZ, Liu Y, Zhong P (2008) Barriers to implementation of cleaner production in Chinese SMEs: government, industry and expert stakeholders’ perspectives. J Clean Prod 16:842–852. https://doi.org/10.1016/j.jclepro.2007.05.002
Silva DAL, Raymundo Pavan AL, Augusto De Oliveira J, Ometto AR (2015) Life cycle assessment of offset paper production in Brazil: hotspots and cleaner production alternatives. J Clean Prod 93:222–233. https://doi.org/10.1016/j.jclepro.2015.01.030
Silvestre BS, Neto S (2014) Are cleaner production innovations the solution for small mining operations in poor regions? The case of Padua in Brazil. J Clean Prod 84:809–817. https://doi.org/10.1016/j.jclepro.2014.01.097
Soylu ÖB, Adebayo TS, Kirikkaleli D (2021) The imperativeness of environmental quality in China amidst renewable energy consumption and trade openness. Sustain 2021 13:5054. https://doi.org/10.3390/SU13095054
The world bank, (2019). Malaysia Overview. World Bank Open Data. https://www.worldbank.org/en/country/malaysia/overview#1 Accessed 16 July 2020.
The world bank, (2020). GDP growth (annual %) - Malaysia | Data. World Bank Open Data. https://data.worldbank.org/indicator/NY.GDP.MKTP.KD.ZG?locations=MY&view=chart Accessed 21 July 2020.
Tiwari A, Singh S, Nagar R (2016) Feasibility assessment for practical replacement of fine aggregate to attain cleaner production perspective in concrete: a review. J Clean Prod 135:490–507. https://doi.org/10.1016/j.jclepro.2016.06.130
Trencher G, Yarime M, McCormick K, Doll C, Kraines S (2014) Beyond the third mission: exploring the emerging university function of co-creation for sustainability. Sci Public Policy 41(2):151–179. https://doi.org/10.1093/scipol/sct044
UNIDO (2021). National Cleaner Production Centers (NCPCs) & Networks. https://www.unido.org/our-focus/cross-cutting-services/partnerships-prosperity/networks-centres-forums-and-platforms/national-cleaner-production-centres-ncpcs-networks. Accessed 25 July 2021.
UNIDO, UNEP (2015) National Cleaner Production Centres 20 years of achievement: towards decoupling resource use and environmental impact from manufacturing growth
UNIP- Universidade Paulista (2020) Production and Environment Laboratory/Laboratório de Produção e Meio Ambiente - UNIP. https://www.unip.br/presencial/ensino/pos_graduacao/strictosensu/lab_producao_meioambiente/apresentacao.aspx. Accessed 12 May 2020
US EPA, (2020a). Air Quality - National Summary | National Air Quality: Status and Trends of Key Air Pollutants | US EPA. Environ. Prot. Agency. https://www.epa.gov/air-trends/air-quality-national-summary Accessed 15 July 2020.
US EPA, (2020b). Our mission and what we do | EPA. Environ Prot Agency. https://www.epa.gov/aboutepa/our-mission-and-what-we-do Accessed 15 July 2020.
US EPA, (2020c). Summary of the Pollution Prevention Act [WWW Document]. Environ Prot Agency. https://www.epa.gov/laws-regulations/summary-pollution-prevention-act Accessed 16 July 2020.
Van Hoof B (2014) Organizational learning in cleaner production among Mexican supply networks. J Clean Prod 64:115–124. https://doi.org/10.1016/j.jclepro.2013.07.041
Vickers I, Cordey-Hayes M (1999) Cleaner production and organizational learning. Tech Anal Strat Manag 11:75–94. https://doi.org/10.1080/095373299107591
Vieira LC, Amaral FG (2016) Barriers and strategies applying Cleaner Production: a systematic review. J Clean Prod 113:5–16. https://doi.org/10.1016/j.jclepro.2015.11.034
Wang L, Huang X, Yu Y, Zhao L, Wang C, Feng Z, Cui D, Long Z (2017) Towards cleaner production of rare elements from bastnaesite in China. J Clean Prod 165:231–242. https://doi.org/10.1016/j.jclepro.2017.07.107
Wesseh PK Jr, Lin B (2015) Renewable energy technologies as beacon of cleaner production: a real options valuation analysis for Liberia. J Clean Prod 90:300–310. https://doi.org/10.1016/j.jclepro.2014.11.062
Wuhan University of Technology (2020) Scientific research: Wuhan University of Technology. http://english.whut.edu.cn/scientficr/bi/ Accessed 05 July 2020.
Yilmaz O, Anctil A, Karan T (2015) LCA as a decision support tool for evaluation of best available techniques ( BATs ) for cleaner production of iron casting. J Clean Prod 105:337–347. https://doi.org/10.1016/j.jclepro.2014.02.022
Yong JY, Klemes JJ, Varbanov PS (2016) Cleaner energy for cleaner production: modeling, simulation, optimisation and waste management. J Clean Prod 111:1–16. https://doi.org/10.1016/j.jclepro.2015.10.062
Yusup MZ, Wan Mahmood WH, Salleh MR, Muhamad MR (2014) The sustainability challenges in the adoption of cleaner production system: a review. J Teknol Sci Eng 70:117–123. https://doi.org/10.11113/jt.v70.2388
Zhang B, Yang S, Bi J (2013) Enterprises’ willingness to adopt/develop cleaner production technologies: an empirical study in Changshu, China. J Clean Prod 40:62–70. https://doi.org/10.1016/j.jclepro.2010.12.009
Zilahy G, Huisingh D, Melanen M, Phillips VD, Sheffy J (2009) Roles of academia in regional sustainability initiatives: outreach for a more sustainable future. J Clean Prod 17:1053–1056. https://doi.org/10.1016/j.jclepro.2009.03.006
Zou H, Du H, Wang Y et al (2017) A review of the first twenty-three years of articles published in the Journal of Cleaner Production: with a focus on trends, themes, collaboration networks, low/no-fossil carbon transformations and the future. J Clean Prod 163:1–14. https://doi.org/10.1016/j.jclepro.2017.04.157
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This work was supported by the Coordination for the Improvement of Higher Education Personnel – Brazil (CAPES) (Finance Code 001); The São Paulo Research Foundation – Brazil (Grant Number 2017/18304-7 and 2019/06077-1); and the National Council for Scientific and Technological Development – Brazil (CNPQ) (Grant Number 312894/2017-1).
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de Mello Santos, V.H., Campos, T.L.R., Espuny, M. et al. Towards a green industry through cleaner production development. Environ Sci Pollut Res 29, 349–370 (2022). https://doi.org/10.1007/s11356-021-16615-2
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DOI: https://doi.org/10.1007/s11356-021-16615-2