An approach to the development of collaborative environmental networks in Colombia

Aproximación a la construcción de redes ambientales colaborativas en Colombia

Patricia Rodríguez-Sánchez1, David González-Cuenca2, Luisa Fernanda Latorre Carrillo3

Recibido: 05/04/2023 | Aceptado: 20/02/2024

Abstract

Research on the creation of Collaborative Environmental Networks (CENs) — industrial ecology, industrial ecosystems and industrial symbiosis — is in the early stage of development in Colombia. This study explores the main elements of the CENs for the development of synergies between actors involved in the productive transformation. The possible benefits and limitations of developing organizational skills through the networks are identified by means of semi-structured interviews, based on a non-probabilistic sample of companies, associations and local governments. Results provide evidence aimed to acquire sustainable knowledge, strengthen skills and awareness of the benefits offered in different markets for participating in CENs. Findings indicate individual interest prevail over the collective wellbeing. The creation of networks of this type is uncommon due to distrust between the actors, which implies that most of them engage in environmental efforts in isolation. This limits the scope of their objectives and the achievement of territorial goals. Policymakers may find guidance on possible organizational links that may contribute to the creation of CENs in the country.

Keywords Environmental management, environmental network, industrial symbiosis, industrial ecosystems, industrial ecology.

JEL Classification
Q01, Q56.

Resumen

Las investigaciones sobre la creación de Redes Ambientales Colaborativas (RAC) -ecología industria, ecosistemas industriales y simbiosis industrial- están en etapa temprana de desarrollo en Colombia. Esta investigación explora los principales elementos de las RAC para la construcción de sinergias entre los actores involucrados en la transformación productiva. Por medio de entrevistas semiestructuradas con muestreo no probabilístico a empresas, asociaciones y gobiernos locales se identifican sus posibles beneficios y limitaciones en el desarrollo de habilidades empresariales en las redes. Los hacedores de políticas pueden encontrar orientación sobre posibles vínculos organizacionales que contribuyan a la creación de RAC en el país.

Palabras clave Gestión ambiental, red ambiental, simbiosis industrial, ecosistemas industriales, ecología industrial.

1. Introduction

Every organization requires resources derived from nature for its operations. However, the excessive use of such resources affects the bio-geo-chemical cycles, which evidently causes environmental degradation with an impact of the sustainability of the global economy (Jahanger et al., 2022). In recent decades, the importance of protecting the environment has led to the execution of business plans aimed at achieving a viable relationship between the ecological systems and economic growth (Gil-Lamata & Latorre-Martínez, 2022) through the conscientious and rational use of resources, and the mitigation of the environmental impacts produced by a company’s operation.

Therefore, each organization should be responsible for the outputs it produces (Gil-Lamata & Latorre-Martínez, 2022), which can be achieved through the improvement of its processes. Since no single organization can individually achieve the sustainability objectives (Fehrer & Wieland, 2021; Patala et al., 2014) and that no organization is an island (Liu et al., 2015), given that it is part of a production chain (Pérez Pravia & Vega de la Cruz, 2021), the joint improvement of processes will have a greater impact, which can be achieved through Collaborative Environmental Networks (CENs).

In this article, the concept of CEN refers to the concepts of industrial symbiosis, industrial ecosystems and industrial ecology, all of which have been the object of extensive academic research as individual concepts, but have not been studied as interrelated concepts (see Figure 1). Since industrial symbiosis is a specific application of industrial ecology (Beames et al., 2021; Herczeg et al., 2018) that can contribute to the sustainability of an industrial system (Ruiz Puente et al., 2015); and where an industrial ecosystem is a community of organizations that participate in an industrial symbiosis (Ashton et al., 2017; M. Chertow & Ehrenfeld, 2012). Consequently, the CENs can be defined as a group of actors that seek, through collective work, to reduce their environmental impacts.

Figure 1. Actions in common of the concepts of industrial ecology, industrial ecosystems and industrial symbiosis.

Source: Prepared by the authors based on (Bolaños Vidal, 2020; M. R. Chertow, 2000; Frosch & Gallopoulos, 1989; Gil-Lamata & Latorre-Martínez, 2022; Górecki, 2020; Herczeg et al., 2018; Kumari & Patil, 2019; Lange et al., 2021; Le Tellier et al., 2019; Lucchetti & Arcese, 2014; Morales et al., 2019; Neves et al., 2019; Tolstykh et al., 2020; Tsujimoto et al., 2018; Zaoual & Lecocq, 2018).

Given that no studies exist that link the concepts of industrial ecology, industrial ecosystems and industrial symbiosis, and the increased development of environmental themes in Colombia, this article explores the key elements for the development of CENs in the country as reference for government, private and public organizations that find it beneficial to work collaboratively. Besides, they are willing to develop networks of this type in order to improve the environmental performance of the production transformation that is required.

This article has four main sections. The first section presents the theoretical framework related to the concepts of industrial ecology (IE), industrial ecosystems (IES) and industrial symbiosis (IS). The second presents the study’s results under the categories of understanding the basic concepts of the networks, the aspects considered for their development, the actors involved, and the benefits and challenges of their configuration. The third and fourth sections present the analysis of the results, and the conclusions, recommendations and future work, respectively.

2. Collaborative environmental networks (CEN)

Industrial ecology (IE), one type of CEN, has been given different definitions (Bolaños Vidal, 2020; Erkman, 2002) due to its dynamic approach (Bolaños Vidal, 2020); however, an early definition refers to a metaphorical relationship between the natural and industrial ecosystems (Frosch & Gallopoulos, 1989). The aim is therefore to restructure an industrial system into a natural system, based on the understanding of its operations, rules and interactions (Bolaños Vidal, 2020; Nuñez-Cacho et al., 2018). IE aims for an industrial system to behave like a natural system, in which balances are present that do not and will not affect the existence of the system itself.

IE also aims for industrial systems to adopt a sustainable approach (Jackson, 2002; Le Tellier et al., 2019; Lucchetti & Arcese, 2014), and to reduce the carbon footprint of organizations (Zaoual & Lecocq, 2018) through the creation of new production models (Walker et al., 2021). Therefore, IE (Bolaños Vidal, 2020; Górecki et al., 2022):

i. Improves the industrial metabolism (Le Tellier et al., 2019; Nuñez-Cacho et al., 2018);

ii. Creates a closed cycle within the industrial ecosystem, for example by using waste as an input for a different process (Górecki, 2020; Le Tellier et al., 2019); and

iii. Reduces the flow of materials (Górecki, 2020).

Another type of CEN is the industrial ecosystem (IES), which is analogous to an IE in that it uses the concept of a natural ecosystem as an analogy to understand the transformation of the industrial ecosystems (Tsujimoto et al., 2018). Therefore, IES refers to the complex network of relationships between organizations, which are often grouped around a main actor that generates and/or processes the waste that is used by the rest of the system (Ayres, 2002).

In other words, IESs focus on waste management – on reducing waste flows – (Kumari & Patil, 2019; Le Tellier et al., 2019; Tolstykh et al., 2020) and on the joint management of resources – efficiency of production lines –, with a focus on the sustainable development of the ecosystem (Kumari & Patil, 2019; Tolstykh et al., 2020). For this reason, IES are organizational relationships that make efficient use of resources and reduce waste, thereby mitigating the negative environmental impacts on the ecosystem.

Lastly, the concept that has been most explored in academic research is another type of CEN, the Industrial Symbiosis (IS), whose definition is derived from the term “symbiosis,” which means the metabolism of biological communities in which independent or non-related species mutually benefit by exchanging materials, energy and information (Dong et al., 2022; Yedla & Park, 2017).

However, there are several definitions of the IS (Boons et al., 2017), concept that refer to organizational collaborative networks (M. Chertow & Ehrenfeld, 2012; Gil-Lamata & Latorre-Martínez, 2022; Herczeg et al., 2018; Jato-Espino & Ruiz-Puente, 2021; Lucchetti & Arcese, 2014; Park et al., 2018; Patala et al., 2014) or working agreements (Velenturf & Jensen, 2016), aimed at effectively managing resources (Boons et al., 2017; M. Chertow et al., 2019; M. Chertow & Ehrenfeld, 2012; Park et al., 2018; Patala et al., 2014; Subramanian et al., 2021) and sharing services and benefits (Boons et al., 2017) through the application of industrial ecology (M. R. Chertow et al., 2021; Herczeg et al., 2018; Mulrow et al., 2017) and the reduction of environmental impacts derived from industrial activities (Boons et al., 2017; Park et al., 2018). Interactions of this type take place between groups or organizations that would normally have no relationships with each other (Farel et al., 2016; Herczeg et al., 2018; Subramanian et al., 2021), because, for example, trading in byproducts is not part of their normal business (Beames et al., 2021; Herczeg et al., 2018).

IS is based on eco-efficiency, cooperation, proximity and resilience (Morales et al., 2019), which enables sharing or exchanging resources (Farel et al., 2016; Lange et al., 2021; Velenturf & Jensen, 2016), services (Farel et al., 2016; Neves, Godina, Azevedo, Pimentel, et al., 2019; Zaoual & Lecocq, 2018), infrastructure, experiences, consulting, equipment, logistics and transportation (Neves, Godina, Azevedo, Pimentel, et al., 2019). The most common are the optimization of energy, materials and waste flows (Morales et al., 2019). For example, the waste and byproducts of one organization become resources of another (Jato-Espino & Ruiz-Puente, 2021; Paquin et al., 2015; Subramanian et al., 2021), which means that IS is predominantly used by the manufacturing industry, to transform materials into new products (Neves, Godina, Azevedo, Ao, et al., 2020; Neves, Godina, Azevedo, Pimentel, et al., 2019).

The motivators for a company to engage in IS are the scarcity of resources (Herczeg et al., 2018; Kara et al., 2022), enhancing the organization’s visibility and strengthening its social identity. These by demonstrating the organization’s social and cultural responsibility, as well as tax credits and reimbursement policies derived from the reduction and recycling of waste (Yu et al., 2014); compliance with environmental regulations, and economic benefits (Herczeg et al., 2018; Kara et al., 2022; Yu et al., 2014), among others (see Table 1). Other stakeholders may also benefit thanks to the creation of new jobs associated with the IS activities, waste reduction and energy efficiency (Beames et al., 2021; Herczeg et al., 2018; Kara et al., 2022).

Table 1. Benefits of industrial symbiosis.

Benefits of industrial symbiosis

Access to new technologies (Yedla & Park, 2017)

Reduction in final disposal costs (Neves et al., 2019, 2020; Paquin et al., 2015; Yedla & Park, 2017) and acquisition of materials (Dong et al., 2022; Herczeg et al., 2018; Neves et al., 2019; Paquin et al., 2015; Yedla & Park, 2017) as sub-products that are less expensive due to their low production costs and availability nearby (Herczeg et al., 2018).

Creation of new markets related to the generated sub-products (Neves et al., 2019; Paquin et al., 2015; Yedla & Park, 2017)

Collective worker education programs (Yedla & Park, 2017)

Reduction and more efficient use of natural resources (Beames et al., 2021; Herczeg et al., 2018; Kara et al., 2022; Neves, Godina, Azevedo, Ao, et al., 2020)

Lower environmental impacts (Herczeg et al., 2018; Paquin et al., 2015), such as a reduction in greenhouse gases (Neves, Godina, Azevedo, Pimentel, et al., 2019), lower waste for disposal (Beames et al., 2021; Herczeg et al., 2018; Kara et al., 2022; Paquin et al., 2015), less pollution and reduction of raw material imports, turning negative externalities into positive ones (Chertow & Ehrenfeld, 2012)

Efficient use of services such as water treatment and landfills (Yedla & Park, 2017)

Lower costs and higher private benefits, as well as the creation of public environmental benefits (Chertow & Ehrenfeld, 2012)

Source: Prepared by the authors based on different authors.

Consequently, by further working on the concepts of IE, IES and IS, it is possible to develop a CEN, if the organization has prioritized environmental aspects (Pinuer et al., 2022), which will enable it to have access to sustainable practices (Yedla & Park, 2017) and create new technologies and solutions to lessen its environmental impacts (Patala et al., 2014). It also help reduce costs through the efficient use of resources (Beames et al., 2021; Herczeg et al., 2018; Kara et al., 2022; Neves, Godina, Azevedo, Ao, et al., 2020; Paquin et al., 2015; Yedla & Park, 2017), and improve the corporate image (Patala et al., 2014).

3. Methodology

This study used a qualitative approach of the descriptive and exploratory type, which started out with a literature review of the concepts of industrial ecology, industrial ecosystems and industrial symbiosis. These concepts were defined and characterized based on the most cited articles since 2015; however, articles from earlier periods that offer major theoretical contributions were also included. Afterwards, we designed the instrument for the semi-structured interviews. This technique was selected to gather the information due to its flexible application, since it offers a general discussion plan with no predefined order (Packer, 2018), and it enables requesting clarifications to the answers given (Pangavare et al., 2022). This technique was used with organizations that voluntarily decided to participate in the study, following a formal invitation, between June and August 2022.

The following criteria were used to select the organizations: i) their location and operation in the Valle de Aburrá or Sabana Central regions, which are highly developed industrial areas in Colombia, and ii) their typology as a manufacturing company, a company that coordinates environmental activities, or the municipal administrative offices responsible for environmental strategies. The sample was non-probabilistic by convenience, for the effects of selecting an easily available population (de Pino Casado & Martínez-Riera, 2022). The interviews were either face-to-face or virtual with senior executives who were highly knowledgeable of the organization, and in some cases, the interviewees filled out the interview form.

Depending on the type of participant, the instruments had either a government or business approach. The former includes categories in the framework of sustainability public policies, such as: relations for sustainability (Beames et al., 2021) and actions and difficulties in implementing public policies (Herczeg et al., 2018; Neves, Godina, Azevedo, Pimentel, et al., 2019; Yedla & Park, 2017; Yu et al., 2014). The latter included categories such as a organization knowledge and its views on working through Collaborative Environmental Networks (Beames et al., 2021; Farel et al., 2016; Herczeg et al., 2018; Kara et al., 2022; Neves, Godina, Azevedo, Ao, et al., 2020; Subramanian et al., 2021; Tolstykh et al., 2020; Yang et al., 2022; Zaoual & Lecocq, 2018). The interview included questions about exchanges of outputs between organizations, the willingness of the players to develop cooperation networks of this type, positive or negative perceptions about its implementation, and the implementation of public policies, among others (Herczeg et al., 2018; Neves, Godina, Azevedo, Pimentel, et al., 2019; Yedla & Park, 2017; Yu et al., 2014). It also included further inquiries regarding any support received from the municipal government.

The study’s participants included an individual actor, 5 coordination associations, 12 companies and 7 municipal administration offices (20 interviews and 4 forms filled out). The interviews were transcribed, coded and analyzed in the ATLAS Ti software. Coding was performed based on the themes of the Collaborative Environmental Networks and the implementation of sustainable public policies, grouped into 4 families and 28 conceptual categories, for a total of 453 codes (see Table 2). Lastly, the results and the analysis enabled the identification of the main elements for the configuration of a CEN, namely the appropriation of the concepts, key aspects for the development of a CEN, actors, benefits and challenges (see Figure 2).

Table 2. Conceptual categories from the analysis of interviews.

Collaboration between academia, business, local administration

Collaboration between business and the local administration

Willingness to work with the local administration

Collaborative Environmental Networks

Views of the local administration on working with academia

Activities to engage with the local administration

Examples of implementation of the circular economy

Network promoters in Valle de Aburrá

Relationship with academia

Support from the local administration

Circular economy plans

Benefits of the networks

 

Communicating events to the local administration

Challenges of the circular economy

Development of networks

 

Inclusion of the local administration

Government views on the circular economy

Willingness to develop networks

 

Failures of the local administration

Government views on the benefits of the circular economy

Participation in networks

 

Willingness to work with the local administration

Government views on the challenges of the circular economy

Government views on environmental networks

 

 

 

Challenges of developing networks

 

 

 

Intermediaries in the network

 

 

 

Network promoters in the Sabana Central Region

 

 

 

Government views on the challenges of networks

 

 

 

Awareness of the benefits offered by the local administration

Source: Prepared by the authors.

Figure 2. Phases of the research methodology.

Source: Prepared by the authors.

4. Results

This section presents the main findings from the process of categorizing the interviews, where the information provided by the business and government participants is listed in the following five (5) sections.

4.1. Appropriation of the concepts for the development of Collaborative Environmental Networks

During the interviews, many terms were commonly used related to CEN; however, as Interviewee 1 pointed out (personal interview, June 13, 2022), new terms appear every day and only those who are interested in these topics understand their meaning. Terms such as circular economy, sustainable business model and green business sound nicer than what can actually be, given the current state of the law, knowledge and economic capacity (Interviewee 27, personal interview, July 21, 2022). For example, they do not clearly understand the meaning of IS, but they associate it with the circular economy (Interviewee 1, personal interview, June 13, 2022), and with collaborative work with one or more companies to create shared value through their processes, products or services (Interviewee 17, personal interview, August 22, 2022).

Some mentioned the need to acquire more knowledge on the concept of the circular economy (Interviewee 30, personal interview, June 16, 2022), and redefining the concepts of efficiency and productivity to include terms such as sustainability and the circular economy (Interviewee 22, personal interview, July 1, 2022); however, none of the responses indicated any appropriation of the terms IE or IES.

4.2. The development of Collaborative Environmental Networks

According to the interviewees, the Collaborative Environmental Networks arise from the need to comply with legal requirements (Interviewee 20, personal interview, July 29, 2022), pressure from customers (Interviewee 25, personal interview, July 12, 2022), or the identification of problems, challenges and opportunities (Interviewee 20, personal interview, July 29, 2022). Additional aspects that promote the development of CENs are indicated in Figure 3.

Figure 3. Reasons why organizations are willing to develop CENs.

Source: Prepared by the authors based on interviews.

The participants indicated that it would not be difficult to develop CENs, as long as they have a clear purpose and the related actors are involved (Interviewee 20, personal interview, July 29, 2022), and that there are clear benefits to be obtained by belonging to the network (Interviewee 7, personal interview, July 21, 2022). However, there are some areas where the organizations are not interested in networks of this type (Interviewee 4, personal interview, July 26, 2022); companies might not cooperate if they do not feel comfortable when another organization benefits from the waste it produces (Interviewee 22, personal interview, July 1, 2022). Some said collaborative work will only take place when confidentiality agreements are in place (Interviewee 1, personal interview, June 13, 2022), which represent challenges for the implementation of industrial ecosystems (Zaoual & Lecocq, 2018).

Confidence in the development of CENs is sometimes eroded when the staff from the local administrations who lead the project leave, which makes it necessary to rebuild the trust of the other actors. They also perceive that the municipal administrations are not genuinely interested in the challenges faced by companies, because they are usually involved in political campaigns and in what they consider politicking (Interviewee 20, personal interview, July 29, 2022).

4.3. Main actors that configure the Collaborative Environmental Networks

Even though several different actors configure a CEN, according to the interviewees the most common are the companies, the municipal governments, academia and intermediaries.

i. Companies often participate in a CEN when: Waste from their process is used by another company (Interviewee 4, personal interview, July 26, 2022; Interviewee 12, personal interview, July 12, 2022; Interviewee 11, personal interview, July 12, 2022; Interviewee 17, personal interview, August 22, 2022; Interviewee 27, personal interview, July 21, 2022); they are suppliers and clients of virtual networks to buy and sell waste raw materials (Interviewee 1, personal interview, June 13, 2022). They also create partnerships with associations of recyclers to manage their waste (Interviewee 1, personal interview, June 13, 2022); they offer training on topics such as obtaining environmental permits and tax incentives (Interviewee 3, personal interview, July 26, 2022, Interviewee 25, personal interview, July 12, 2022; Interviewee 29, personal interview, July 12, 2022).

They also receive advice and assistance on different environmental topics (Interviewee 27, personal interview, July 21, 2022) that promote sustainable practices (Interviewee 18, personal interview, July 27, 2022), and offer educational activities to children and youth to raise awareness on the generation and adequate management of waste (Interviewee 1, personal interview, June 13, 2022).

ii. The Municipal Government. Even though the government organizations do not create CEN themselves (Interviewee 13, personal interview, June 29, 2022), there is a company-government relationship, though it is limited to: Task groups to formulate government plans (Interviewee 11, personal interview, July 12, 2022), mandatory meetings to demonstrate the community’s participation in the events (Interviewee 11, personal interview, July 12, 2022; Interviewee 20, personal interview, July 29, 2022); charging fines or taxes (Interviewee 4, personal interview, July 26, 2022, Interviewee 14, personal interview, July 26, 2022); and when there is specific interest in using a company’s services for political activities (Interviewee 4, personal interview, July 26, 2022; Interviewee 13, personal interview, June 29, 2022).

iii. Academia is important for CENs because of its contributions on environmental matters (Interviewee 25, personal interview, July 12, 2022; Interviewee 13, personal interview, June 29, 2022); however, there were conflicting views, in the sense that some interviewees acknowledge the work they do in promoting the creation of government-business-academic networks (Interviewee 10, personal interview, June 28, 2022), whereas other interviewees claim that academia is not willing to work in a network (Interviewee 19, personal interview, July 25, 2022), or that otherwise a time comes when academia no longer fits into the organizational dynamics (Interviewee 2, personal interview, July 12, 2022).

iv. The intermediaries promote the participation of companies in the CENs (Interviewee 13, personal interview, June 29, 2022), and enable the coordination of efforts and the solution of disputes between parties (Interviewee 17, personal interview, August 22, 2022). Some interviewees also believe that this role should be taken on by the government (Interviewee 11, personal interview, July 12, 2022), or by a non-profit organization (Interviewee 1, personal interview, June 13, 2022). However, this role is usually taken on by a private entity (Interviewee 11, personal interview, July 12, 2022).

4.4. Benefits of participating in Collaborative Environmental Networks

One of the challenges for developing collaborative networks is to pinpoint their actual value (Interviewee 1, personal interview, June 13, 2022; Interviewee 4, personal interview, July 26, 2022; Interviewee 11, personal interview, July 12, 2022;). However, the interviewees also point out both monetary and non-monetary benefits from developing CENs (see Chart 1).

Chart 1. Monetary and non-monetary benefits of CENs.

Monetary benefits

Non-monetary benefits

• Receive tax benefits (Interviewee 11, personal interview, July 12, 2022; Interviewee 20, personal interview, July 29, 2022; Interviewee 30, personal interview, June 16, 2022).

• Monetary benefits (Interviewee 11, personal interview, July 12, 2022).

• Capital investment derived from project development (Interviewee 14, personal interview, July 26, 2022; Interviewee 19, personal interview, July 25, 2022).

• Investment in fixed assets (Interviewee 18, personal interview, July 27, 2022).

• Lower rates for different services (Interviewee 17, personal interview, August 22, 2022).

• Lower costs of raw materials derived from waste (Interviewee 1, personal interview, June 13, 2022).

• Training and technical support (Interviewee 23, personal interview, August 22, 2022);

• Technology transfer (Interviewee 9, personal interview, June 22, 2022);

• Improve the organization's reputation (Interviewee 17, personal interview, August 22, 2022; Interviewee 20, personal interview, July 29, 2022), for example, through certifications (Interviewee 1, personal interview, June 13, 2022; Interviewee 15, personal interview, June 22, 2022),

• The development of market networks that enable the creation of new businesses (Interviewee 9, personal interview, June 22, 2022; Interviewee 22, personal interview, July 1, 2022), offer products/services through the network and transcend to new public relations (Interviewee 7, personal interview, July 21, 2022).

Source: Prepared by the authors.

4.5. Challenges in the development of Collaborative Environmental Networks

The interviewees repeatedly mentioned four challenges for the development of CENs, three of which involve relations with other actors: coordination between organizations, the exchange of waste or byproducts and the relationship with the local administration. The fourth is related to the economic difficulties involved in implementing a CEN. The following are additional details on these challenges:

i. Coordination with other organizations is often difficult because individual interests prevail over the collective wellbeing (Interviewee 20, personal interview, July 29, 2022). Corporate efforts are predominantly carried out in isolation (Interviewee 4, personal interview, July 26, 2022; Interviewee 11, personal interview, July 12, 2022; Interviewee 22, personal interview, 1 de July, 2022).

ii. Some of the limitations to exchanging waste or byproducts include the organizations’ lack of knowledge of the waste products they can provide or receive (Interviewee 7, personal interview, July 21, 2022) and how such waste can be actually processed (Interviewee 9, personal interview, June 22, 2022). This is due to the low level of capacity to acquire technology and the lack of research and development teams (Interviewee 18, personal interview, July 27, 2022), and that the economic benefits from exchanging waste are not perceived, which implies that no one is willing to take on certain costs, such as transportation (Interviewee 1, personal interview, June 13, 2022). Additionally, promoting the use of materials of this type may be difficult when their price or visual appearance are not better than traditional materials (Interviewee 1, personal interview, June 13, 2022), or having to assume that the product is of lower quality, which implies that its price should be lower (Interviewee 8, personal interview, July 12, 2022).

iii. The relationship between CENs and local administrations is perceived as being weak, because they believe that political interests prevail over the collective benefit (Interviewee 19, personal interview, July 25, 2022) and companies often quickly cut off the relationship if they are not assigned top priority in fulfilling their needs (Interviewee 31, personal interview, June 29, 2022). Local administrations often focus solely on providing environmental consulting or training (Interviewee 8, personal interview, July 12, 2022; Interviewee 13, personal interview, June 29, 2022; Interviewee 14, personal interview, July 26, 2022), mainly with an approach that focuses on economic growth (Interviewee 5, personal interview, June 28, 2022; Interviewee 18, personal interview, July 27, 2022).

iv. At the company level, they perceive economic difficulties because of lack of awareness of the economic benefits offered by the local administrations (Interviewee 3, personal interview, July 26, 2022; Interviewee 4, personal interview, July 26, 2022; Interviewee 14, personal interview, July 26, 2022; Interviewee 24, personal interview, July 25, 2022). They also claim that investment costs are generally high (Interviewee 4, personal interview, July 26, 2022; Interviewee 11, personal interview, July 12, 2022; Interviewee 22, personal interview, July 1, 2022), including the fees for participating in the networks (Interviewee 17, personal interview, August 22, 2022; Interviewee 23, personal interview, August 22, 2022; Interviewee 29, personal interview, July 12, 2022).

5. Results analysis

5.1. Appropriation of the concept for the implementation of Collaborative Environmental Networks

One of the main elements for the implementation of a CEN is the appropriation of the concept by the actors involved in the network. Regarding the CEN, they suggest that the local population needs to understand the concepts of clean production, industrial ecology and circular economy (Liu et al., 2015), as well as the concept of (Park et al., 2018). It was found that the interviewees could identify the terms, but only one interviewee defined IS as a collaboration network between organizations (M. Chertow & Ehrenfeld, 2012; Herczeg et al., 2018; Jato-Espino & Ruiz-Puente, 2021; Lucchetti & Arcese, 2014; Park et al., 2018; Patala et al., 2014).

The understanding of the concepts associated with CENs is a key starting point, because it enables each actor that decides to participate in the network to understand the ultimate objective of applying each concept. Without such understanding, it is highly likely that adequate action will not be taken, because of the ambiguous and unfounded knowledge base. It may also be the case that production processes may be outdated, that irrelevant information is used, that efforts will be made in aspects that are not key priorities, and that a snowball effect of errors in the network can occur.

5.2. The development of Collaborative Environmental Networks

A key element for the development of a CEN is the willingness to establish close working relationships based on trust, openness, a spirit of cooperation, codes of conduct and confidentiality, to enable addressing the environmental challenges (Zaoual & Lecocq, 2018). Based on such agreements, it is possible to set the network’s objectives, even when the participants have different interests (see Figure 4).

The construction of mutual trust is the basis for fulfilling the agreements established in a CEN. It must also be accompanied by a culture of empathy, in which the benefit of the territory prevails over the organization’s self-interest. Even though the interviewees indicated several reasons that would motivate them to participate in a CEN (see Figures 4 and 5), a low level of trust is also perceived (Interviewee 1, personal interview, June 13, 2022; Interviewee 4, personal interview, July 26, 2022; Interviewee 20, personal interview, July 29, 2022). This represents a key deficiency according to several authors (Farel et al., 2016; Herczeg et al., 2018; Neves, Godina, Azevedo, Pimentel, et al., 2019; Zaoual & Lecocq, 2018).

On the other hand, if such a culture is actually created and it permeates all the actors of a CEN, the active and committed participation of each member would be achieved, which would undoubtedly produce significant benefits on several fronts (business, ecological, social and territorial, among others).

5.3. Main actors that configure the Collaborative Environmental Networks

In previous points, important elements for the development of a CEN were mentioned, such as the appropriation of the basic concepts associated with a CEN, the importance of the actors’ declaring their intention to participate based on values such as trust, and the need to agree on the objectives of the CEN, taking into consideration the participants’ interests.

The participating actors of a CEN can be (Boons et al., 2017): industrial actors, intermediaries (Tolstykh et al., 2020; Zaoual & Lecocq, 2018), and government actors (Park et al., 2018). It would be reductionist to assume that only companies should comprise a CEN, because there is room in them for different actors, whose roles within the network depend on their objectives and their level of responsibility. However, it is essential that they all benefit in order to ensure ongoing participation. The development of a CEN implies creating growth opportunities and benefits in different areas, such as the transfer of knowledge (Bellantuono et al., 2017; Tolstykh et al., 2020; Zaoual & Lecocq, 2018), technology (Bolaños Vidal, 2020; Neves, Godina, Azevedo, Pimentel, et al., 2019; Patala et al., 2014; Tolstykh et al., 2020) and the exchange of waste (Yedla & Park, 2017; Zaoual & Lecocq, 2018), among others.

Regarding participation by the government, Mulrow et al. (2017) hold that government support is an important factor for the success of an IS, as in enables formulating strategies, and developing and implementing action plans based on learning from such experiences (Boons et al., 2017). This promotes the development of national policies that provide incentives for industries to participate in CENs (Herczeg et al., 2018; Neves, Godina, Azevedo, Ao, et al., 2020; Neves, Godina, Azevedo, Pimentel, et al., 2019; Yedla & Park, 2017). Even though academic experts acknowledge the importance of governments as players that drive and promote the relationships of an industrial symbiosis, the actions of the local governments are not aligned with this approach. The municipal administrations have focused on the creation of small spaces to promote water and solid waste management, but they do not promote environmental management instruments such as certification, ecolabel, environmental programs or plans, and tax incentives to promote sustainable production through CENs.

Additionally, if organizations are not willing to create CENs, it becomes essential to have an intermediary to coordinate, manage interests and ensure alignment between the actors (Zaoual & Lecocq, 2018). However, the interviewees have differing opinions on who should take on this role. If the intermediation is taken on by a government agency, it can contribute by launching educational programs, building adequate infrastructure and creating incentives for these activities (Bellantuono et al., 2017); whereas if it is taken on by a private or public third party, it can promote a transparent market to exchange resources, transfer tactical knowledge, share experiences, and fulfill the role of communicator of the lessons learned from symbiosis activities carried out elsewhere to replicate them locally (Boons et al., 2017).

For this reason, it is considered that an intermediary would facilitate the development of a CEN, by focusing solely on carrying out activities that enable the creation of a culture of support, organizing the various actors, and ensuring that good relations prevail in terms of transparency and the wellbeing of all the participants.

Ideally, the intermediary should be a government entity, because it would always act in a neutral manner, as long as external economic interests do not influence its political interests. However, if this is not possible, it should be an organization that, even though it is paid for its work, looks out for the benefit of its clients, which are the network participants. It should also be responsible for carrying out diagnoses to enable the identification of the environmental activities to be implemented jointly by the organizations, to subsequently lead and materialize possible partnerships.

5.4. Benefits of participating in Collaborative Environmental Networks

Both academics and the interviewees identify several benefits derived from networks of this type. In economic terms, the benefits of CENs are the revenues derived from the sale of the waste produced by the organization (Neves, Godina, Azevedo, Pimentel, et al., 2019; Paquin et al., 2015; Patala et al., 2014; Yedla & Park, 2017), the substitution of raw materials and their lower transportation costs (Yu et al., 2014), and lower waste disposal costs (Neves, Godina, Azevedo, Ao, et al., 2020). According to the interviewees, additional benefits are related to tax credits, capital or fixed asset investments, discounts on services offered by network members, the commercial value of the waste produced, and opportunities to engage in business relationships between the actors, among others. Both academics and the interviewees agree agree that the lower costs of raw materials produced from waste is an economic benefit. CENs promote sharing of information and knowledge (Tolstykh et al., 2020; Yedla & Park, 2017) and of experiences (Neves, Godina, Azevedo, Pimentel, et al., 2019), which help promote sustainable practices (Yedla & Park, 2017).

In non-economic terms, these three elements were not frequently mentioned by the interviewees, but they are significant benefits of CENs: obtaining environmental certifications (Li et al., 2015), improving the organization’s reputation (Patala et al., 2014; Yu et al., 2014) and the creation of networks and distribution markets (Walker et al., 2021). Consequently, we may conclude that the interviewees mainly focus on the economic aspects (see Figure 5), but are not aware of the impacts of the labor and energy markets (Beames et al., 2021; Herczeg et al., 2018; Kara et al., 2022).

5.5. Challenges in the development of Collaborative Environmental Networks

Some of the challenges for implementing CENs include: not knowing the potential value of the creation of a collaborative network; non-existence of a formula to achieve IE, because the exchanges that take place in one context cannot be automatically implemented in another; the absence of records of the economic, social and ecological benefits of IE; negative perceptions on the use of waste as inputs; and the low level of trust between the organizations (Zaoual & Lecocq, 2018). Other challenges include differences in the interests and objectives of the various actors (Patala et al., 2014), lack of knowledge by suppliers and clients of the properties of the waste, and the high costs of transportation, equipment and infrastructure (Neves, Godina, Azevedo, Pimentel, et al., 2019).

The interviewees in fact agree with the academics in pointing out the challenge of the differing interests among the actors, the ultimate goal of developing environmental networks, and the lack of knowledge of the properties and characteristics of the waste to enable its commercialization. However, the biggest concern is the high investment costs that the production transformation implies in order to implement a CEN. Consequently, it is necessary, in each territorial and cultural context, to identify the challenges and benefits of developing a CEN, in order to define effective strategies to support the various actors.

6. Conclusions, limitations and future research

The construction of CENs is in an early stage of development in Colombia, as is the case of many leading-edge environmental topics. Given that their benefits and requirements are widely unknown, this study was aimed at identifying the key elements for the creation of CENs, as the basis for the consolidation of synergies between different actors.

The findings suggest that it is necessary to develop business skills for the appropriation of knowledge on the various concepts involved in CENs, and even though this article only focuses on three (3) of these concepts (industrial ecology, industrial ecosystems and industrial symbiosis), many more may arise depending on a CEN’s objectives. It is also necessary to communicate the possible sustainability impacts from participating in a CEN, such as its impact on the labor market by creating job opportunities, or its contribution to the energy mix from the use of waste for energy generation by the industries (Beames et al., 2021; Kara et al., 2022; Morales et al., 2019).

Some of the key elements for the creation of CENs are the development of common objectives for its participants, acknowledging and agreeing on each participant’s role in the network, and creating interactions and synergies depending on each member’s capabilities and interests. It was found that companies are the main actors in the network because they are responsible for the production transactions; however, they should not ignore or exclude the possibility of other participants such as the academic sector, the municipal government and coordination associations, among others, as facilitators for the creation of CENs. The findings indicate the creation of networks of this type is uncommon due to distrust between the actors, which implies that most of them engage in environmental efforts individually, which limits the scope of their objectives and the achievement of territorial goals.

Some limitations are the scare studies in Colombia on the application of the links between industrial ecology, industrial ecosystems and industrial symbiosis; besides, there is no centralized information available on the activities that are being performed by the territories, especially by local governments, which implies that there is no context in this regard. This study was carried out in a specific territorial context, which implies that no generalizations can be made from its results. Another limitation was that fieldwork reflected the organizations’ distrust in handling information; they did not share specific information on their processes, such as the inputs and outputs of each link of their value chain, or the actors that participate in this chain. Consequently, the analysis was limited to opinions rather than to facts or potential cooperation partnerships, which accentuates any biases in the opinions of the interviewees, who may not be aware of all the organization’s processes. However, strategies may be developed to achieve the participation of different members of the organizations, in order to promote possible CENs that involve all the levels of the organizational structures.

In future studies, it would be important to further assess how each of the presented concepts can be applied in the country, and how CENs are linked to the new environmental dynamics in the framework of the circular economy and its associated public policies. Similarly, due to the scarce development of the theme, the delimitation of the CEN concept is ambiguous, and even though the participants identified some of the key elements for developing CENs, it is important to work further on the criteria that define them, for example, their characteristics, functions and the impact of the actors in the framework of a CEN, possible types of relationships and measurement and performance indicators. It is important to define the elements that would enable rating an implemented CEN as successful in a given territorial context.

7. Acknowledgments

This research is financially supported by the Vicerrectoría de Investigaciones from Universidad Militar Nueva Granada and the Universidad EAFIT. It is a result from project INV-DIS-3446 validity 2021. The authors also gratefully acknowledge Professor Juan Gregorio Arrieta Posada for his helpful collaboration.

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1 Distance learning Faculty, Universidad Militar Nueva Granada, Colombia. Email: patricia.rodriguez@unimilitar.edu.co

2 Distance learning Faculty, Universidad Militar Nueva Granada, Colombia. Email: david.gonzalez@unimilitar.edu.co

3 Distance learning Faculty, Universidad Militar Nueva Granada, Colombia. Email: luflatorreca@unal.edu.co