Skip to main content
Advertisement
  • Loading metrics

Integrating climate mitigation and environmental peacebuilding objectives through sustainable land use systems: Theory of change and indicators

  • Héctor Morales Munoz ,

    Roles Conceptualization, Data curation, Formal analysis, Funding acquisition, Investigation, Methodology, Resources, Supervision, Validation, Visualization, Writing – original draft, Writing – review & editing

    hectorcamilomorales@gmail.com

    Affiliations International Center for Tropical Agriculture CIAT, Cali, Colombia, Leibniz Centre for Agricultural Landscape Research (ZALF E. V), Müncheberg, Germany, Department of Agricultural Economics, Humboldt University of Berlin, Berlin, Germany

  • Leigh Martens,

    Roles Conceptualization, Investigation, Writing – original draft

    Affiliation Past Global Changes (PAGES), Bern, Switzerland

  • Katharina Löhr,

    Roles Methodology, Supervision, Writing – review & editing

    Affiliation Leibniz Centre for Agricultural Landscape Research (ZALF E. V), Müncheberg, Germany

  • Michelle Bonatti,

    Roles Conceptualization, Methodology, Supervision, Writing – review & editing

    Affiliations Leibniz Centre for Agricultural Landscape Research (ZALF E. V), Müncheberg, Germany, Department of Agricultural Economics, Humboldt University of Berlin, Berlin, Germany

  • Julian Chara,

    Roles Validation, Writing – review & editing

    Affiliation Centro para la Investigación en Sistemas Sostenibles de Producción Agropecuaria CIPAV, Cali, Colombia

  • Lisset Perez,

    Roles Data curation, Formal analysis, Investigation, Software, Validation, Visualization, Writing – review & editing

    Affiliation International Center for Tropical Agriculture CIAT, Cali, Colombia

  • Stefan Sieber,

    Roles Funding acquisition, Project administration, Supervision

    Affiliations Leibniz Centre for Agricultural Landscape Research (ZALF E. V), Müncheberg, Germany, Department of Agricultural Economics, Humboldt University of Berlin, Berlin, Germany

  • Augusto Castro-Nunez

    Roles Conceptualization, Project administration, Supervision, Writing – review & editing

    Affiliation International Center for Tropical Agriculture CIAT, Cali, Colombia

Abstract

Land is an essential natural resource for climate mitigation and peace. It is commonly connected with sources of GHG emissions and with drivers of (violent) conflict. Therefore, climate mitigation and peacebuilding strategies are co-designing sustainable land-use systems (SLUS) with affected communities to integrate land-based climate mitigation and peacebuilding objectives. SLUS is practiced within agricultural production systems that meet sustainability principles (environmental, social, and economic). Nevertheless, there needs to be more program evaluation frameworks, especially measurable indicators, that integrate these two objectives (achieving peace and climate mitigation). This study aims to develop a methodology and criteria to evaluate the precise mechanisms of SLUS influencing greenhouse gas (GHG) emissions and drivers of conflict. A mix-method approach was used in two case study regions, Cesar and Caquetá, Colombia, where SLUS strategies where implemented. First, we conducted three workshops, two in-person and one virtual (n = 103). Secondly, we held semi-structured interviews (n = 115) to make an analysis of the conflict. Our research focused on the drivers of land-based emissions and conflict drivers targeted by the SLUS implementation. Lastly, through a household survey (n = 929), we illustrated the impacts of SLUS in peacebuilding at the farm level. Results show that SLUS, such as cocoa agroforestry, can contribute to climate change mitigation and deliver co-benefits in four core factors: (i) socio-economic inclusion by creating jobs and diversifying livelihoods, (ii) dialogue and conflict transformation by allowing negotiations around the participatory design of farms, including conservation agreements, (iii) natural resource governance, and (iv) cooperation by creating knowledge exchange and a community of practice.

1. Introduction

Land plays a critical role in GHG emissions in the tropics. Article 5 of the Paris agreement stresses the importance to mitigate climate change through land use activities. Drivers of conflict [1] and post-war contexts [2] are also influenced by land use activities. After a peace agreement, the most readily available assets to kick-start post-conflict stabilization and recovery are often natural resources such as land [3]. Therefore, many peacebuilding strategies are targeting the land-use sector and delivering Sustainable Land-Use Systems (SLUS) as a means to provide livelihoods to affected communities [4,5]. SLUS embody various agricultural practices, technologies, and resource management strategies tailored to specific farm and landscape contexts. These systems promote the production food in a sustainable manner. They can store carbon and mitigate risks from natural hazards; offer cultural values; support critical ecological functions such as nutrient and water cycling, filtering, and buffering; and are central to farmers’ economic vitality and survival [6]. Therefore, several efforts to reduce GHG emissions in the tropics target the land-use sector and aim at delivering SLUS as a means to provide alternative livelihoods [7].

The international community and the global governance systems represented by different United Nations agencies have put forward different strategies to separately mitigate the effects of climate change Sustainable Development Goals (SDG13) and build peace and stability in fragile countries (SDG 16) [8,9]. However, climate change and conflict are deeply interconnected in their causes and solutions [10]. For instance, actions to build peace can create the enabling environment for cooperation around climate mitigation and adaptation [7,11]. Meanwhile, climate change adverse effects and climate adaptation and mitigation strategies could be indirect drivers of conflict by increasing food insecurity or restricting land uses, which may also have a multiplier effect augmenting the likelihood of social unrest and violence, especially in agricultural-dependent communities and fragile contexts [1215].

Efforts to reduce land-based emissions include safeguards oriented to prevent unexpected social, environmental, and development outcomes. Global initiatives have been developed with the aspiration of achieving land-based emissions reductions (Paris Agreement of 2015) and restoring landscapes (Bonn Challenge of 2011). These initiatives include financial mechanisms to reduce land-based emissions, such as Reducing Emissions from Deforestation and forest Degradation (REDD+), fostering conservation, sustainable management of forests, and enhancement of forest carbon stocks in tropical countries.

However, as countries with the potential for reducing land-based emissions are emerging from or experiencing conflict, such initiatives need to coordinate peacebuilding and mitigation strategies to be successful. An example of theses overlapping challenges is Colombia that have suffered from prolonged conflict and is increasingly becoming a source of land-based GHG emissions [16]. The Colombian government is aware of potential synergies between policies for peacebuilding and policies for climate change mitigation in the land sector [17]. Particularly, because agricultural (including illicit crop cultivation) and cattle ranching activities practiced in conflict-affected areas are important drivers of GHG emissions associated with deforestation and landscape degradation [18]. Although other land-use changes can be a source of GHG emissions, deforestation (i.e. changes from native forests to other land uses) is the single most important source of GHG in Colombia, with 19.2% of total emissions in 2018. The impact of other land-use changes represented less than 1% in the same period [19]. To achieve the reduction of GHG emissions however, will require understanding existing barriers typically present in conflict and post-conflict areas, and peacebuilding measures, such as those related to weak state presence, land-use competitions between legal and non-legal activities and limited access to markets [20,21].

An approach that integrates climate and peace objectives are SLUS. They constitute an entry point to integrate efforts to reduce land-based emissions with those for achieving peacebuilding objectives in areas affected by land-related conflicts, which are the most common type of conflicts in tropical regions [7]. For instance, SLUS can incorporate REDD+ social and environmental safeguards, such as acknowledging the priorities and ownership of local communities, national and local policies for climate mitigation, and a conflict-sensitive approach that enables co-design with local communities [22]. It goes in line with the promotion of natural resource management. Natural resource management refers to managing natural resources such as land, water, soil, plants, and animals [23]. Authors claim that the goal of natural resource management should not be to handle or control only ecosystems but rather, to enhance humans’ interactions with the surrounding environment in a sustainable manner [24,25].

Despite the linkages between land use, carbon emissions and peace there is a lack of program evaluation frameworks that integrate these sectors [26,27]. Attempts have been made within the field of environmental peacebuilding, which integrates similar objectives in the fields of environment, conflict and peace. It is defined as the multiple approaches and pathways by which the management of environmental issues is integrated in and can support conflict prevention, mitigation, resolution and recovery [15]. This field has expanded in the literature, and current debates recognize that monitoring and evaluation (M&E) in environmental peacebuilding is a topic that will help understand when interventions achieve their climate and peace objectives, when they do not, and why. For example, attribution in environmental peacebuilding has been a challenge in matching interventions with outcomes. Some authors emphasize the importance of understanding land-related tensions before external actors implement any effort to improve land sustainability and access to avoid unintended consequences [2]. Other authors argue that potential impacts on peacebuilding should also be assessed in the frame of climate mitigation initiatives as co-benefits beyond merely preventing environmental and social risks [4,2830]. Therefore, the added value of having programming and evaluation frameworks that integrate climate mitigation and adaptation goals and peacebuilding is that such frameworks can take into account not only the unintended consequences of climate mitigation projects, but they will proactively and consciously take into account peacebuilding activities [4]. Furthermore, how a specific intervention contributes to one another, enhancing their impacts. In the same line, climate change consequences and peacebuilding interventions interact with a broad range of socio-economic, gender and political factors, which integrated environmental peacebuilding interventions can address [31]. Finally, developing more sophisticated, consistent and widespread M&E tools in environmental peacebuilding will provide accountability and learning for beneficiaries, implementers and funders [15].

The underlying dynamics of SLUS and how they can contribute to mitigation and peacebuilding are not well understood. The document aims to develop indicators to monitor whether environmental peacebuilding has been successful. Our main research question is: How is the implementation of SLUS contributing to climate change mitigation and peacebuilding in Caquetá and Cesar, Colombia?”

The subsequent section presents the methodological design. Consequently, the results section consists of both a context and a conflict analysis conducted with SLUS members and stakeholders to determine existing drivers of conflict that can be affected by the interventions. Further, mechanisms for understanding SLUS’s contributions to peacebuilding are presented. Thereafter, we present a set of indicators for measuring the contributions of SLUS to climate mitigation and peacebuilding. The following section discusses the results in light of the existing literature on environmental peacebuilding. The final section concludes and recommends possible uses of the research.

2. Materials and methods

2.1. Case study description

This study demonstrates the clear overlapping challenges of climate and conflict risks in Colombia [16]. Colombia was selected because of its high deforestation rates and its emergence from a long history of conflict. The Colombian armed conflict has lasted for over 60 years, having, as a consequence, over 9 million victims [32]. Colombia has the highest rate of internally displaced people in the continent and massive damages to its natural environment including unsustainable resource use and exploitation, illicit crops, soil erosion, deforestation, destruction and contamination of water sources. These factors also impact other activities perpetuating a vicious loop such as forced displacement, land appropriation and indiscriminate logging [33,34]. In 2016, the Colombian Government (GoC) and the Revolutionary Armed Forces of Colombia (FARC) signed a peace agreement, including essential goals relating to sustainable rural development of conflict-affected areas. Additionally, the GoC has expressed its commitment to the Paris agreement, the Aichi Targets and the 20x20 land restoration initiative. Achieving these national priorities implies developing sustainable land-use systems as integral to moving beyond the conflict that has plagued the country for the past 50 years [35]. However, during the post-peace agreement period (2017–2018), the area of forest disturbance increased by 50% (about 238 000 ha) across the Andes-Amazon Transition Belt in comparison with the four-year peace negotiation stage (2013–2016). Using remote sensing data sets, researchers have identified and mapped forest disturbance. Among the reasons are the withdrawal of FARC’s informal governance structures of control over forested areas, and the consequent entrance of actors such as drug cartels, large landowners and dissidents who cleared forests with expectations of favorable land tenure policies. It increased large-scale cattle ranching, coca cultivation dispersal, and speculative illegal land markets. Many lands are overutilized, indicating worsening soil degradation [18,3638]. Since then, according to the Institute of Hydrology, Meteorology and Environmental Studies (Instituto de Hidrología, Meteorología y Estudios Ambientales—IDEAM), deforestation rates have stabilized, dipping to 197,159 hectares cleared in 2018, and under 158,894 hectares lost the following year[39]. Furthermore, the violence against environmental and social leaders have been staggering. According to the international NGO Global Witness, 2021 marks the second year in a row Colombia registered the most killings nationwide (65 only during 2020), despite government promises to increase security in rural areas and offer activists protection [40].

The areas chosen for this study are the departments of Cesar and Caquetá. We selected these regions because they present geographical overlaps between priority areas for forest conservation, climate change mitigation and peacebuilding. Caquetá shows high deforestation rates and political violence due to the prolonged presence of the FARC guerrilla as one of the foremost perpetrators leaving a high volume of victims of violence. Cesar presents high rates of soil degradation and violence from paramilitary groups and the presence of rebel groups, with high numbers of victims of violence as well. Farmers in these two regions of the country have a strong sense of identity. They have been significantly affected by the armed conflict through illegal drug trafficking and natural resource exploitation [41]. Both regions are rich biodiversity hotspots with a high sensibility to climate change and a low resilience capacity to cope with risk, especially with regards to the management of land and water [42,43]. Furthermore, these regions have a strong presence from armed groups; therefore, many citizens have been displaced, and earned their livelihoods by cultivating illegal crops or working in the informal mining sectors. As a result, this rapidly changed the social dynamics creating social unrest, an impoverished economic situation, environmental degradation, deforestation, and loss of biodiversity. Over the years, the widened disparities and inequalities have put a heavy strain on individuals, families, communities and institutions [44,45]. Both regions are highly dependent on agricultural activities for their economic development, thus sustainable land uses are essential to cope with environmental and social vulnerabilities [21] (Fig 1).

thumbnail
Fig 1. Geographical location of Caquetá and Cesar in Colombia.

Base layer source: Sistemas de Información Geográfico para el Ordenamiento Territorial—IGAC.https://sigot.igac.gov.co. Global Administrative Data v3. https://gadm.org. Red regions represent the departments of interest, Caquetá and Cesar.

https://doi.org/10.1371/journal.pclm.0000075.g001

2.1.1. Caquetá.

Caquetá is located in the south of Colombia along three climatic regions: Piedemonte Amazónico, Central Amazonía and Southwest Amazonia, spanning over two significant ecosystems, the Andes and the Amazon, which provides extraordinary biodiversity with the territory [43,46]. Caquetá represents an ideal case study for integrating climate mitigation and peacebuilding because it represents climate and conflict vulnerability intersections [4]. On the one hand, the armed conflict has affected its civil population, around 122,000 people are registered in the region as victims of forced displacement [47]. The FARC controlled de facto many of the social, economic and political aspects of vulnerable rural regions, including income and land use [48]. After the peace agreement, strategic areas were liberated from guerrilla control and different actors began entering the region to invest in mining and agribusiness [49]. Furthermore, FARC dissidents and other criminal gangs are now present in Caquetá, aiming to control coca, gold and timber production [50].

From another perspective, Caquetá is a unique biodiversity hotspot corridor with vast flora and fauna native to the region [48]. Four national parks are located in Caquetá, safeguarding about 25,000 square kilometres of rich biodiversity and abundant sources of water feeding the Amazon basin, including large parts of the iconic Serranía de Chiribiquete [51]. However, Caquetá’s population growth was historically fueled by dispossessed farmers escaping from the bi-partisan political violence (liberal vs conservatives) of the 1950s and the armed conflict between the FARC rebels and the government in the 1970s [52]. Many were even motivated by governmental policies that promised to give titles to people who moved with plans to ’clean land’ in the Amazonian wild forest. They could then establish farms (fincas), hoping to gain officially recognized title to the land [53]. Moreover, Caquetá concentrates around 47% of forest loss in the Colombian Amazon, where agriculture and cattle ranching increased by almost 40% from 1999 to 2017 [54]. The establishment and eradication of illicit crops, deforestation for building infrastructure for the oil industry, extractive mining, and cattle ranching are among the drivers of deforestation causes in Caquetá [55]. Nevertheless, cattle ranching is an important source of income for the department’s rural populations [21].

2.1.2. Cesar.

Cesar is located in the northeast of Colombia, has an area of 22,000 km2 divided into five ecoregions; the Serranía del Perijá mountain range, the Cesar River valley, the Sierra Nevada de Santa Marta mountain range, the Magdalena river valley and the Cienaga de Zapatosa marshes complex [42]. Along with its multitude of rivers and fertile soils, the mountain systems from the Serranía del Perijá and the Sierra Nevada de Santa Marta make the land suitable for a great variety of agricultural activities. Among these are extensive cattle ranching, palm oil plantations, and the production of maize, coffee, and rice [56]. In the 2010s coal mining had a boom and became the main economic activity in Cesar [57]. According to the Colombian Geographic Institute (Instituto Geográfico Agustín Codazzi IGAC), over 63% of the soil is inadequate to use. As a consequence, 81% of the soil present some degree of erosion [58]. The armed conflict has heavily impacted Cesar. Due to its natural resource richness, many armed groups have directed their activities in this territory. The National Liberation Army (Ejército de Liberación Nacional—ELN Spanish) and the FARC have attacked mining infrastructure; far-right paramilitary and drug trafficking groups concentrated their territorial control between 1996 and 2006, affecting the land distribution and displacing vulnerable rural populations [59]. In Cesar, the influx of the armed conflict, specifically paramilitary violence, is considered "pro-business" [60]. Meaning that land accumulation, monopolies, and unsustainable land uses such as massive coal mining and large cultivations were supported by paramilitary forces [61]. For example, the mining company Drummond has been officially acused by the national prosecutor office to have financially supported the leaders of the United Self-Defense Forces of Colombia (Autodefensas Unidas de Colombia, or AUC, in Spanish), who were located in the coal mining areas in the north of the department of Cesar [62]. Furthermore, agricultural practices and unsustainable land uses have been associated with episodes of violence. For example, according to research conducted by the governmental institution national center for historical memory, between 1971 and 2018, 112 members of different trade union organizations in the palm oil industry in Cesar were murdered in association with the presence of paramilitary groups in the region [63]. In the post-agreement, palm oil production has also been associated as an essential driver of both social conflicts and ecosystems degradation [37]. Currently, after two peace agreements, one in 2005 with the paramilitary group AUC and a second one with the FARC rebels in 2016, the Cesar department still suffers from violence carried out by armed groups and narcotraffickers who stand behind land owners and political elites who opposed land restitution reclamations carried out by victims of the armed conflict, human right activist and environmental defenders [64,65].

2.2. The sustainable land uses systems approach

We use the case of SLUS implementations in the departments of Caquetá and Cesar as the two regional nodes for piloting the SLUS approach in Colombia [66]. The SLUS approach is adequate to analyze the interconnections of climate mitigation and peacebuilding. The SLUS approach incorporates practices at different scales, not only conducting changes at the farm level but intervening at the landscape level and on value chain governance. Broader changes are implemented with financial and non-financial incentives and market approaches, such as climate finance and zero-deforestation incentives [67]. Such implementations’ outputs are expected to reduce land-based GHG emissions, conserve forests, restore degraded landscapes and improve rural livelihoods.

The SLUS implementation that we analyze in this research is cacao agroforestry systems (CAFS). CAFS are complex multi-species cropping systems where cacao trees are associated with other permanent or temporary crops and woody tree species. Furthermore, the CAFS seek to integrate people, their culture and interactions with one another in farming and forest [68]. In Colombia, cacao crops are particularly relevant because they have existed for many years and recently, they have been promoted as an alternative for coca production [69]. They are established and managed under a canopy of trees by smallholder farmers with differing production practices dependent upon climate, soils, and household conditions. CAFS tend to include banana plants, fruit trees, and shade trees, mainly with timber specie [70].

In Colombia, cocoa is not a primary driver of deforestation. Instead, different stakeholders have promoted cocoa as a sustainable livelihood alternative to coca production and, more recently, as a crop that can help reduce the pressure on forests that emerged after the peace agreement from other land uses, such as extensive cattle ranching [71]. Recently, the national government and the Tropical Forest Alliance have signed voluntary agreements with five economic sectors, including cocoa, intending to get different actors involved in the chains to commit to eliminating their deforestation footprint along the supply chain. The signing of the zero-deforestation agreement for cocoa, "Cocoa, Forests and Peace", took place in 2018 and builds on the experience of the World Cocoa Foundation, which has developed model agreements in Ghana and Côte d’Ivoire. The agreement, supported by international development agencies, has contributed to increasing the planted areas and improving the quality of the bean, allowing it to be positioned globally. As a result, Colombian cocoa has now been recognized as "fine flavour cocoa" by the International Cocoa Organisation (ICCO) [72]. However, in a post-peace agreement context, cocoa systems must overcome existing barriers, such as weak state presence, land-use competitions between legal and non-legal activities and limited access to markets [71].

The SLUS project agreed with the Colombian Cocoa Federation (FEDECACAO Spanish acronym) to sustain the work piloting organic agroforestry cacao. The agreement allowed a baseline survey (n = 929) to understand and document the current farmers’ socioeconomic and environmental conditions and characterize their CAFS farming practices to analyze the enabling conditions and determinants of adoption of SLUS and improve management practices in Caquetá and Cesar [73]. Afterwards, a new agreement was reached with farmers’ associations to pilot a batch of certified organic cocoa from producer organizations in the municipalities of La Paz, Cesar (n = 25) and Belén de Los Andaquíes in Caquetá (n = 25). Cocoa value chain committees were formalized with stakeholders of the dialogue platform, and local beneficiaries took part in the training on integrated cocoa management. The committees enabled the farmers to define their priorities and co-design this pilot project.

SLUS works at various scales. First, at the farm scale, SLUS requires a prioritization exercise with the farmers to choose the best CAFS practices that work for forest conservation, enhance sustainable livelihood alternatives and diminish the risk of conflict. Second, the SLUS project embraces work at the value chain scale. This is under the recognition of local governance systems and the importance of dialogue among different stakeholders along the whole value chain as a critical factor in aligning with national and global priorities [74].

2.3. Methodological framework

We applied a mixed-methods approach based on three research phases: (i) Conflict analysis: World Café with key stakeholders in Caquetá (n = 54) and Cesar (n = 30), semi-structured interviews (n = 115) and a Do No Harm workshop (virtual) (n = 19). (ii) Development and validation of theory of change and indicators: virtual workshop (n = 19). (iii) Pilot testing of indicators: household survey for illustrating peace-related indicators implementation (n = 929: Caquetá n = 429 and Cesar n = 500) (Fig 2).

2.3.1. Phase 1. Context analysis and conflict sensitivity.

We used two methods to identify the current conflict and deforestation drivers according to communities’ perceptions and to understand how a SLUS implementation can contribute to addressing those drivers.

2.3.1.1. World Café. The "World Café" approach is a conversational process that promotes building trust, constructive dialogue, and collaborative learning. Whilst initially, the World Café method is a tool widely used as a participatory method for citizen participation and organizational change processes, it also gains in importance as a methodological approach to collecting qualitative data [75,76].

We conducted two workshops using the ’World Café’ methodology in Florencia, Caquetá (n = 54), and Valledupar, Cesar (n = 30) at the end of 2019. Each workshop lasted around five hours, with breaks and refreshments provided. Both of the workshops were conducted in Spanish. The World Café has three stages. The first introduces the participants, the methodology and a glossary of terms (including environmental peacebuilding, socio-environmental conflict, community governance and SLUS). In the second stage, participants are asked to position themselves at one of the three tables/subjects (environmental peacebuilding, community governance and SLUS), each table consists of about ten people. Materials such as cards and note paper are provided, consisting of two rotations, each rotation lasting 45 minutes. Participants decided freely on which group to start and were told they were free to switch groups.

The first rotation involves listing the past and present socio-environmental conflicts, their drivers and possible ways to solve them. Socio-environmental conflicts are those focused on the incompatibility of the use of natural resources and the impacts on the environment by different social groups [77]. The second rotation explores the future scenarios and the prioritization of the central conflict drivers of deforestation and local socio-environmental conflict that a SLUS could impact. For prioritization, the participants had three votes per person that they could allocate to any of the drivers listed. The third stage was a plenary to present and discuss the results of the exercise.

We used this method because the World Café facilitates intimate exchange, disciplined inquiry, cross-pollination of ideas, and possibility thinking. Its conversational process helps groups engage in constructive dialogue around critical questions, build personal relationships, and foster mutual learning [75]. By changing tables after a defined period, participants always meet other participants, learn from their previous conservation round and can bring thoughts from their preceding discussions. Thereby, the participants exchange much information and agreements for prioritization can grow [76]. Further, it provides an excellent opportunity to initiate conversation in large and diverse groups, in our case, bringing together local stakeholders, including representatives of governmental organizations, farmers’ associations, indigenous communities, and local experts in environmental conservation and peacebuilding.

2.3.1.2. Conflict sensitivity: Do no harm. Conflict sensitivity is an approach that attempts to minimize unintended negative impacts in conflict-affected environments. A conflict-sensitive analysis is an essential building block to understanding the complex layers of conflict. Using the do no harm approach is relevant in this case because it allows for finding possible sources of conflict and successful peacebuilding outcomes within climate mitigation interventions [78].

This methodology is based on conflict context analysis, building on seven steps that start with an understanding of the sources of tension (dividers) and the local capacities for peace (connectors) and concludes with a testing process of the impact of the initiatives [79]. These guidelines should help organizations better understand: i) the conflict dynamics in the region, ii) how their interventions interact with those dynamics, and iii) what are the necessary steps needed in order to ensure their work reduces adverse outcomes and increases positive ones [78]. In this research, we implemented an adaptation of this approach. We developed a new category of "peace opportunities", which is the result of designing adaptations or solutions to activities that may impact increasing the dividers or sources of tension.

A do no-harm analysis was conducted in a virtual workshop held on 25 July 2020, with 19 local experts from the SLUS project to identify a contextualized theory of change for assessing peacebuilding impacts. The workshop started with a presentation about peacebuilding definitions, the cycle of conflict and the Do No Harm approach. Consequently, we presented the conflict drivers extracted from the World Café, and the local experts prioritized conflict drivers by voting. We asked the participants to prioritize drivers according to their evaluation of existing local conflict dynamics possibly affected by SLUS. Each participant had three votes that could be given to any driver.

2.3.2. Theory of change and indicators development.

A theory of change describes how and why an initiative would work based on the best available information [80]. The theory of change presented in this study is based on:

  1. The main objectives and assumptions of how SLUS interventions contribute to peace.
  2. The results of a contextualized conflict analysis: Conflict and deforestation drivers and how each activity contributes to diminishing those drivers (do no harm analysis).

To develop the theory of change and indicators, we recovered previous research conducted in the same project that identifies factors and mechanisms to assess environmental peacebuilding [4]. Furthermore, seven key factors and corresponding indicators were identified from this basis, along with stakeholders’ workshops (see Tables 4 and 5).

In the virtual workshop, the participants were asked to identify the central dividers or sources of conflict that can result while implementing CAFS. Then, they identified the possible connectors or factors that bring social cohesion and motivate trust and cooperation during the implementation process. Finally, they identified peace opportunities or strategic action to proactively address conflicts and build dialogue for a successful implementation of the CAFS. The local experts discovered the central assumptions about how SLUS activities affect specific peacebuilding dimensions by identifying the connectors and how to counter the dividers. Finally, the participating local experts identified indicators to measure the peacebuilding contributions of SLUS over time and assess them according to validity, region-sensitivity, and usability [81].

Semi-structured individual interviews were conducted with different stakeholders of the cocoa value chains (CVC) of Cesar and Caquetá to gain more profound knowledge about the possible outcomes of SLUS interventions at the value chain level. The CVC was chosen because the National Government and international development agencies have prioritized cocoa cultivation as an alternative for substituting illicit crops and integral rural development [71,82].

The total sample was 115 actors who provided information on 92 organizations. The interviews took place between 18 November 2020 and 22 February 2021. The sampling design for the semi-structured interviews in each department followed non-probability sampling methods. Firstly, a quota design was used, which sought to select a representative population sample by establishing a proportion to be reached for all the segments that make up the population. In this case, the segments correspond to the relevant stakeholders of the cocoa value chain. The proportion to be reached for each segment was determined either by saturation of the information or by interviewing at least half of the actors or institutions identified [83]. In total, 82 semi-structured interviewees answered questions regarding conflict and peacebuilding in Cesar (n = 58) and Caquetá (n = 24). The average duration was 40 minutes.

2.3.3. Pilot testing of indicators.

To test key indicators, we conducted a quantitative household survey. We surveyed nine hundred and twenty-nine (929) households, Caquetá (n = 429) Cesar (n = 500) of smallholder cocoa farmers in both study regions. We cover 13 of 16 municipalities in the Caquetá department and 18 of 26 municipalities of the César department. We used a random sampling strategy in the entire array of associated producers that implemented some form of cocoa agroforestry. In this study we present the farmers’ perceptions captured by the survey about the contribution of agroforestry systems to peacebuilding in three factors, dialogue spaces, trust and cooperation. The interview was face-to-face in Spanish, based on a closed-ended survey questionnaire. We collected data from March 2021 to Jun 2021. The duration of each interview was approximately 40 minutes. Participation was voluntary, and farmers responded freely and under prior informed consent.

2.4. Limitations

The study has two types of limitations. The first is the social desirability bias, which is a bias in the responses of workshop participants, who, due to possible social pressure, may prioritize the drivers of conflict or deforestation that are most socially accepted [84]. It can happen even among practitioners. We also recognize that there may be biased limitations in the interpretation of participants’ responses. We controlled for this through iteration rounds in the workshops (World Cafe) and by validating the answers with the semi-structured interviews that we conducted individually. Due to the Covid-19 pandemic, we conducted virtual workshops, which can hinder the levels of interaction in a discussion. For example, non-verbal communication is limited. However, virtual scenarios have also been found to hinder unconscious bias from stereotypes such as race and gender [85].

Another limitation is in the pilot to test the peacebuilding indicators. We should clarify that the household survey results illustrate farmers’ perceptions of the impact of implementing a cocoa agroforestry system on peacebuilding factors. However, we are not comparing the conditions and variables of implementing agroforestry systems or the change compared to other agricultural practices. We suggest that further research be made to measure this perception once improvements to these agroforestry systems are implemented to see a change in baseline data. Regarding the theory of change and indicators development, even though the peacebuilding factors and the assumptions of how a slus can contribute to peace are grounded in the literature, there is a lack of more consistent and robust data about the mechanisms of natural resource management to contribute to peace. In this way, our theory of change complements the existing knowledge to a certain degree, ratified by local actors implementing the project; however, local implementers may have a desirability bias for showing early victories, thus leaving out other factors that are also important for enhancing peacebuilding drivers.

4. Results

4.1. Context analysis and drivers of conflict and deforestation

In order to answer the question of how and how much SLUS contribute to peacebuilding, it was essential to determine the different drivers of conflict and deforestation in their specific local contexts, at the farm and value chain levels. Following are the results of the in-person consultations with stakeholders at the world cafe:

4.1.1. Stakeholders’ prioritization of drivers of conflict and deforestation.

In the case of Cesar, the stakeholders reported different drivers of conflict and deforestation. From industrial pollution to desertification due to lack of environmental education. However, most participants identified three key drivers: environmental malpractices such as forest logging and burning, corruption in environmental authorities and conflicts around water resource management (Fig 3). Various environmental malpractices are related to the processes of agricultural expansion. The local experts reported during the workshop that a mentality of unsustainable land uses and exploitation of natural resources dominated development pathways. Such mentality is a combination of economic elites wanting to exploit the land for commercial purposes and a lack of knowledge of local communities to implement sustainable agricultural production practices. For example, local elites established an increase in extensive cattle ranching, carbon extraction and rice monoculture as the primary economic development activities in the region. An important driver of conflict, which also emerged as a consequence of environmental degradation, is the conflict around water management. Stakeholders informed that water management becomes a vital issue because of the ecosystem’s characteristics (tropical dry-forest), exacerbated due to climate change’s adverse consequences, unsustainable land uses and land access. The best grounds are those that have stable water sources. Unfortunately, as reported by the local stakeholders, large-scale agricultural production has used these lands unsustainably, and environmental authorities do not effectively restrict unsustainable water uses.

thumbnail
Fig 3. Prioritization of socio-environmental conflicts in Cesar.

Source: Own elaboration based on workshop in Cesar (n = 30) S1 Data.

https://doi.org/10.1371/journal.pclm.0000075.g003

In the case of Caquetá, the stakeholders prioritized deforestation as a driver of conflict, followed by land grabbing and extensive cattle ranching (Fig 4). Stakeholders recognized that the latter two are simultaneously drivers of conflict and deforestation. Similarly, land grabbing by different groups (e.g. political elites, landless farmers, armed actors) has traditionally been a way of accessing land through the “colonization” and "cleaning" of wastelands or unexplored lands within the Amazon rainforest. "Colonization" is a term used in Colombia to describe the conquest of peasants coming from the Andes known as "colonos" entering into the Amazon region, changing the landscape and establishing farms and villages. The peasants, often victims of political violence, arrived in this region in the seventies motivated by governmental policies encouraging “cleaning land” in jungle “wastelands” to access land titles. Land tenure concerns peasants and indigenous people who have been settled for more than three decades in the region and have not yet formalized their titles. Later on, land-use conflicts arise around expanding agricultural and livestock activities within areas set aside for nature conservation by the national government. The central government did the establishment of some protected areas with little consultation with the local communities ignoring the existent history of occupancy by peasants and the need of these communities to use the forest for the forest their livelihoods [86]. All stakeholders share concerns about oil and mining exploitation in the area. They know the department’s vast water resources and see these extractive activities as a significant threat in the next ten years. They fear that since some areas are no longer affected by the armed conflict, oil and mining companies may want to exploit natural resources, which would seriously impact water sources and the vast biodiversity. Therefore, other economic models of land and forest use that integrate conservation and agricultural production are seen as a great opportunity.

thumbnail
Fig 4. Prioritization of socio-environmental conflicts in Caquetá.

Source: Own elaboration based on workshop in Caquetá (n = 54) S1 Data.

https://doi.org/10.1371/journal.pclm.0000075.g004

4.1.2. Semi structured interviews. Conflict and peacebuilding in the Cocoa Value Chains (CVC) of Cesar and Caquetá, Colombia.

In the interviews, we asked whether the structure and dynamics of the cocoa value chain have given rise to resentments or grievances in the past that became violent or have the potential to become violent in the future. In Caquetá, only one person answered in the affirmative and the rest said no. The person that answered in the affirmative referred to potential conflicts in the cooperatives but no significant disputes. However, in the case of Cesar, it is possible to find conflictive situations around water and its use with the harvest, a situation that worsens in the dry season. In Cesar, 43% of the interviewees said that the cocoa value chain might have water access and management conflicts. Many said that “there is a lack of water concessions by the regional water authority Corpocesar”. Rural territorial planning also brought problems when decision-makers developed a new value chain using land uses unsuitable for the activity. Finally, respondents recognized that violent displacement had brought issues to the department. For example, possible conflicts can happen if people are dispossessed and encouraged by the transitional justice mechanism of land restitution to return to their land and find others that have already bought the ground, but the seller was not the owner. It is significant for the research because it is crucial to tailor the different technical interventions to fragile contexts, such as the studied regions emerging from a conflict and trying to transition to peace.

Regarding CAFS’ peacebuilding contributions. The actors in both departments agree that, in the post-conflict period, “Cocoa has been an inclusive alternative for generating income for peasants”. Among the participants are mainly victims of the armed conflict and farmers cultivating illegal crops. Thus, contributing to regional peacebuilding through the opportunity to cut dependences on illicit crops. Furthermore, the stakeholders said it could create dialogue spaces and foster cooperation and intra-communal social cohesion. Respondents highlighted that the cocoa sector had received much support from the Colombian Government and international development. This recognition implies for both regions and their vulnerable peasants’ population the rise of opportunities for improving their livelihoods in case they can fairly connect to markets. Farmers in both regions mentioned that the cocoa value chain can also “motivate and integrate younger generations into the rural work, preventing their involvement in illegal activities”. The interviews with stakeholders of the cocoa value chain highlight the potentialities of a crop suitable for forest protection and agricultural production, which does not create social tensions and supports regional peacebuilding initiatives.

4.1.3. Conflict sensitivity and Do no Harm approach in SLUS implementations.

We presented the following drivers derived from the world café with local stakeholders to the SLUS project members in the virtual workshop. We asked SLUS project members to prioritize three conflict drivers, which are related the most to SLUS project interventions (Table 1).

thumbnail
Table 1. Votes for the top three drivers of conflict in Caquetá and Cesar, Colombia.

https://doi.org/10.1371/journal.pclm.0000075.t001

4.1.4. Do no harm virtual workshop: Understanding the connectors and dividers.

In the workshop, we asked relevant project members what they could foresee in the SLUS’ step by step implementation as potential connectors (capacities for peace) and dividers (sources of tension) to understand the context further. The workshop exercise with SLUS collaborators permitted identifying how they co-designed each specific pilot implementation with the communities. SLUS project members identified different connectors or capacities for peace within the regions (Table 2).

They are clustered in three main factors, i. participation / co-design ii. Spaces for dialogue. Exchange and cooperation, and iii. Co-benefits of climate mitigation and trust and cooperation. The participants reported that the project implements its intervention with a participatory approach at the farm level. The co-design of the different technologies allows ex-change and cooperation at the community level since a community of practice is built. For example, when a committee of "environmental leaders" is created to monitor animal species, these people generate a sense of ownership and collaborate to enforce the signed nature conservation agreements via social pressure. Communities of practice generally make people respect agreements out of conviction and feel more identified with making initiatives work over time. At the value chain level, the participants mentioned that mapping all the actors within the CVC is vital. This allows the actors to have equal participation and voice in the design of cero deforestation developments. Because actors mapping in the value chain is the first step to creating policies for value chain development. A consensual diagnosis of the actors’ roles in a value chain opens up spaces for dialogue around price negotiations between firms and suppliers. According to a stakeholder: "These new spaces enable the participation of farmers that usually do not have a saying in price negotiations", for example. Further down the path, the government can facilitate the exchange between buyers and suppliers and grant incentives and regulations to multinationals to develop value chains with sustainability standards such as zero deforestation and respect for labour rights. Companies can pay price premiums and, in return, may receive tax concessions. Besides, the SLUS members reported a set of potential dividers or sources of conflict (Table 3). They were clustered into three groups: i. exclusion, ii. Individualistic culture, and iii. Expectations. The participants argued that it is imperative to be transparent and clear when choosing the farms to intervene, presenting valid criteria for identifying beneficiaries. On a similar note, participants mentioned that if the incentives are not maintained when signing deforestation agreements with the farmers, it could create a perverse incentive to reactivate deforestation. Therefore, it is crucial to lower some expectations in particular interventions at the farm level.

Another reported divider was the individualistic culture of the farmers as a barrier for implementing SLUS and connecting farms in a landscape. This divider is attractive because the participants also mentioned that a participatory approach might bring down individual farmers’ barriers and create a sense of community. The SLUS collaborators also identified the strategies to lessen the dividers and enhance the connectors.

4.2. A theory of change for measuring SLUS contributions to peacebuilding

Fig 5 explains the theory of change of how the SLUS project would contribute to climate change mitigation and peacebuilding. Specifically, how SLUS implementation at the farm and value chain levels responds to the existing deforestation/degradation and conflict drivers in Caquetá and Cesar, Colombia. As seen above, SLUS project implementation seeks to address three main drivers of deforestation and conflict, intervening at the farm and value chain level. However, factor number 3 (absence of the state in the territories) falls out of the project’s main goal and direct scope because they neither intend to replace the government nor offer public services.

thumbnail
Fig 5. Theory of Change for SLUS co-benefits to climate change mitigation and peacebuilding.

Source: Authors own elaboration based on literature revision and workshop’s results.

https://doi.org/10.1371/journal.pclm.0000075.g005

The theory of change for SLUS intervention is formulated as follows.

IF SLUS builds capacity, grants investment in rural communities to improve agriculture and extends monetary incentives via conservation agreements with farmers at the farm level THEN, the forest can be successfully conserved, along with water, soils, and other natural resources upon which all people depend for their food, air, water, shelter, and different basic human needs, enabling lasting conditions to improve local communities’ wellbeing. BECAUSE by bringing people together around SLUS co-design and developing inclusive business models in the cocoa value chain, farmers’ socio-economic inclusion is ensured, and a community of practice is established, promoting trusted relationships and preventing conflicts around natural resources.

This theory of change presented in Fig 5 shows the expected outcomes from the specific interventions (Sustainable Agricultural Practices and Net Zero Value Chain Development) represented in co-benefits for climate change mitigation and peace. Furthermore, it recognizes the possible contextual risks present in the implementation areas, as exposed by the project members and stakeholders. For example, when the national or regional government does not grant water access, it could put an external risk that falls out of the scope of the project’s intervention. However, when it is recognized that a possible source of conflict is access, use and management of water. The project can implement irrigation technologies and promote water use, and management plans appropriate to the context to prevent conflicts. Additional activities can also be promoted. For example, the project can advise governments on generating investments and water governance policies that promote new crops as a local peace-positive and development strategy based on promising value chains, including institutionalized mechanisms to solve water-related conflicts. Another example is the importance of building dialogue and association capacities among farmers to foster better results at the value chain level.

4.2.1. How to measure contributions?

Based on this research, seven core factors structure the possible contributions of SLUS to climate mitigation and peacebuilding: sustainable livelihoods, food security, conflict transformation and dialogue, increasing trust and cooperation, gender balance, political and social participation and building institutions for natural resource management.

Tables 4 and 5 show the operationalization of the theory of change. It summarizes the effects of selected SLUS interventions into climate change mitigation and peacebuilding factors, their assumptions, and the indicators to measure the expected outcomes considering the SLUS project intervention and how the peacebuilding factor is affected by the intervention.

thumbnail
Table 4. Peacebuilding factors, mechanisms and indicators at the farm level.

https://doi.org/10.1371/journal.pclm.0000075.t004

thumbnail
Table 5. Peacebuilding factors, mechanisms and indicators at the value chain level.

https://doi.org/10.1371/journal.pclm.0000075.t005

4.3. Household survey: SLUS contribution to peacebuilding

We present the descriptive results of a survey of 429 farmer households in Caquetá and 500 in Cesar by illustration. We asked farmers about their perception, at the societal level, of three peacebuilding factors: the opening of spaces for dialogue, cooperation and conflict resolution. The surveys show that the performance of agroforestry systems impacts the three. First, most agroforestry systems have increased the spaces for community dialogue. To the question, in the process of implementing the agroforestry system, have the spaces for dialogue at the community level increased? 261 households in Caquetá responded affirmatively, and one 168 responded negatively. In the case of Cesar, 358 responded positively and 142 negatively (Fig 6).

thumbnail
Fig 6. Agroforestry has increased community dialogue spaces.

https://doi.org/10.1371/journal.pclm.0000075.g006

Second, the SLUS contributes to reducing conflicts over access to natural resources. According to the survey, 59.4% of Caquetá 255 households consider that SLUS decreased disputes over access to natural resources in their environment and 65.2% in Cesar, corresponding to 362 families (Fig 7). This is significant because one of the risk factors identified in the do no harm workshop was the water access and management conflicts.

thumbnail
Fig 7. Agroforestry has reduced conflicts over access to natural resources.

https://doi.org/10.1371/journal.pclm.0000075.g007

Finally, the implementation of SLUS also effectively contributes to cooperating with other community members. 251 of the total interviewed households in Caquetá responded positively, and 359 of five hundred 500 in Cesar (Fig 8). The survey results show that a majority of people perceive that implementing CAFS within the SLUS approach has opened new spaces for dialogue, prevented conflicts over natural resource management and helped community members cooperate with each other. According to the respondents, implementing these systems contributes to peacebuilding at the community level in a progressive manner. It starts with creating more dialogue spaces to solve conflicts peacefully, and the second step is an amount of cooperation initiatives started as a result of the new spaces.

thumbnail
Fig 8. Agroforestry has enabled cooperation with other community members.

https://doi.org/10.1371/journal.pclm.0000075.g008

5. Discussion and conclusion

This study shows that SLUS designed for climate mitigation can contribute to peacebuilding. According to the reported theory of change, SLUS affects three core factors. That is (i) socio-economic inclusion, (ii) conflict transformation and dialogue, and (iii) Building institutions for natural resource management. The proposed indicators address the most relevant contributions where SLUS project interventions in Caquetá and Cesar affect the drivers of deforestation and conflict, such as extensive cattle ranching and inefficient water use, which is in line with the literature [50,71,87,88]. However, structural drivers such as land access colonization and lack of governance structures are out of the scope of these kinds of projects.

5.1. SLUS increases socio-economic inclusion

First, creating sustainable livelihoods that promote the socio-economic stabilization of an area after a peace agreement has been signed is fundamental to sustaining peace [89,90]. Second, since rarely the governance scenarios to plan and scale-up SLUS are neutral [4,9193], a conflict sensitivity analysis of connectors and dividers works best when carried out in a participatory manner among a group of actors involved in the process, directly or indirectly. It is essential to develop strategies for conflict transformation, including co-design solutions and capacity building in negotiation to avoid unintended effects. Third, SLUS pilots’ implementation shows that its approach to natural resource management, including the cocoa value chain scale, fosters environmental peacebuilding, as several authors discuss [9496]. It is essential to include vulnerable populations (e.g. rural women and youth), ex-combatants and other groups of the territory to foster social cohesion. Furthermore, natural conservation agreements must be co-designed with farmers reconciling economic needs, food security and environmental protection, thus increasing trust, social cohesion and resilience against illegal economies and violence [97]. Income generation and fostering ownership in a group or community of practice can contribute not only to generating resources with which families can reject involvement in illegal economies [98]. In addition, it generates mutual aid systems, social networks and informal community support mechanisms that help reduce vulnerability. Further, they can extend their activities to manage early warnings and social denunciations of armed threats.

The research shows that the co-design of sustainable livelihoods using conflict-sensitivity enhances sustainability impacts. In line with the literature, SLUS implementations at the farm level take account of sustainable agricultural practices as an alternative to extensive cattle ranching or even illegal crops [99]. Conservation agreements by farmers with a participatory approach contribute to forest protection and natural restoration, the way in which the farms are designed. Convening community meetings to jointly decide on the type of arrangements on the farm and the best techniques to improve production generated a sense of belonging to a community of practice on the farms in Caquetá. This feeling gives people a positive reception to the productive projects of agroforestry cocoa. They see it as an initiative that is a product of the peace agreement with the guerrillas and favorable to consolidating a climate of peace that also improves production alternatives that do not involve deforesting the forest (S1 Data). Second, scaling SLUS based on participatory approaches creates spaces of dialogue to sign conservation agreements for climate change mitigation and ex-change knowledge among farmers and relevant stakeholders. At the farm level, these dialogue scenarios build trust facilitating cooperation among peers. Third, institutional arrangements that promote access and effective management of natural resources impact sustainable solutions for climate mitigation and contribute to peacebuilding by promoting participatory mechanisms and inclusion of vulnerable populations (e.g. victims of the conflict, youth, ethnic minorities and rural women). Fourth, creating employment within a net zero-deforestation CVC at the cocoa value chain level is critical to improving livelihood and diminishing grievances and rural populations’ participation in armed conflict. The proposed indicators help assess participation in dialogue spaces to create equal and horizontal zero-deforestation value chains and participation of vulnerable populations such as rural youth and women.

However, root causes of conflict such as land access and the lack of presence of the government are factors where SLUS intervention may not directly impact. The contribution of SLUS does have the potential to coordinate policies from environmental and agricultural authorities after land restitution programmes or rural development plans. These factors are also expected to be considered among different stakeholders’ platforms such as value chains, governmental agencies and actors engaged in climate mitigation, adaptation and peace promotion to up-scaling SLUS. More importantly, the SLUS and value chain upgrading strategies need to inform existing local development plans and enhance the capacities of local and national government officials, safeguarding possible sources of conflict such as water access and land tenure insecurity.

According to the results, SLUS interventions present an opportunity to design new sustainable agricultural practices that contribute to the global goals of climate change mitigation. At the national level, SLUS provides opportunities for local farmers to enhance their income and detach themselves from the risks posed by illegal economies [3]. This goes in line with the literature about socio-economic inclusion. It implies improving the terms on which individuals and groups participate in society, improving those disadvantaged’ ability, opportunity, and dignity [100]. Further, valuing and preserving local culture and heritage while providing jobs to farmers (both men and women) at the individual/household level and integrating their production schemes to ecological and deforestation-free value chains contributes to long-term peacebuilding. Furthermore, it corroborates the assumption that creating sustainable livelihoods after conflict parties sign a peace agreement is fundamental to stabilization [101].

The connection of the factor of socio-economic inclusion created by SLUS also has to do with its dissemination and up-scaling. Since most of the up-scaling of SLUS require a transfer of knowledge, the implementation of SLUS aims to take into account local knowledge and cultural practices at the farm level. Further, one of the key activities is to promote knowledge exchange between farmers and other stakeholders. This approach may foster dialogue scenarios and the opportunity of farmers to cooperate among them, embracing social cohesion and a culture of peace [74].

5.2. SLUS contribute to conflict transformation and dialogue

The results corroborate that SLUS in the form of agroforestry systems reduces conflicts around natural resources. Also, the participatory approach creates dialogue spaces where trust acts as a social lubricant that enhances and optimizes the climate outcomes. It aligns with the literature about conflict transformation where solving a conflict imply recognizing different cultures and interest and addressing relationships, attitudes, behaviours, interests and discourses in violence-prone conflict settings through creating dialogue processes [102,103]. Thus, the new dialogue spaces where communities are actively involved in decision-making for implementing sustainable agricultural practices to reduce deforestation contribute to build better societal relations based on mutual recognition, knowledge exchange and dissemination for solving common challenges [4].

5.3. Building institutions for natural resource management

The results show that SLUS interventions at the farm level promoting forest conservation agreements with farmers contribute to protecting forest patches reducing biodiversity loss, and mitigating CO2 emissions. The critical assumption of SLUS agrees with the literature since the governance and inclusive institutions for managing natural resources are essential factors to grant success in a project implementation related to tackling climate mitigation and peacebuilding. Evidence shows that weak natural resource governance triggers adverse social outcomes and conflict [104]. Significantly in conflict-affected scenarios, creating and reconstructing existing local and new governance scenarios is key to scaling agroforestry practices and creating an inclusive agricultural value chain [105]. This process needs to facilitate transparent, open processes so that every community member understands his or her rights the systems and methodologies set in place. For example, in Cesar, the study shows that implementing a conflict-sensitive approach is crucial to understanding local governance structures and preventing extensive resource-intensive agriculture interventions (such as extensive cattle ranching) that may affect natural resources already under pressure, such as water sources. Therefore, it is important to dedicate activities to understand how the institutions or ‘rules of the game’ structure the power, benefit, and responsive relationships between state agencies, local agencies, the people, and other stakeholders [106]. Another crucial factor is ensuring the nexus between conservation and delivery of local socio-economic benefits associated with natural resources, where multiple stakeholders are involved, ‘institutions’ (formal and informal) are required to structure patterns of interaction [107]. In Caquetá, for example, a unifying factor among many stakeholders is the recognition that the region’s wealth is its vast water availability and that a development model based on agro forestry systems is better than extractive industries of mineral or oil. Furthermore, implementing community inclusion, public participation, and fostering inter-sectorial dialogue are vital approaches for incentivizing long-term investments that protect soils, biodiversity, and ecosystem services [108,109].

Finally, it is worth mentioning that while the SLUS approach is being developed in post-conflict contexts and as a way to prevent conflict, there are fundamental limitations concerning broader governance issues, such as regional water management. Furthermore, there is a risk that SLUS generate depoliticized discussions that do not touch on some of the deeper reasons for armed political conflicts [93]. Even essential issues in the Colombian armed conflict context such as land reform and land access are apparent constraints in the SLUS approach. However, under conditions of legal security and to strengthen the implementation of land access or illegal crop substitution programs, it has excellent potential. Similarly, to extrapolate the results to policy arena it is important that local governments recognize the implementation of SLUS and take advantage of financial mechanisms such as the UN REDD+ [4,30,110113]. The international community and the local governments must recognize the importance of conflict-sensitivity approaches acknowledging the local context and the communities’ priorities (ownership and participation). UNFCCC’s safeguards (e.g. REDD+ safeguards) and land-based climate change efforts implemented in areas affected by armed conflicts should ideally consider United Nations’ peacebuilding principles to reduce the risk of a relapse into conflict: i) address drivers and root causes of conflict, including those related to inequity in the access to natural resources and income; ii) build institutions and capacities of individuals, communities and authorities to manage conflict and deliver services; iii) enhance social cohesion and build trust among social groups; and iv) build trust in and legitimacy of governments.

In this line of thought, any intervention to address climate change and conflict should recognize ways to apply these principles and make them traceable in monitoring and evaluation frameworks. Further research should be conducted to test and tailor further the proposed indicators in other contexts where conflicts and grievances around natural resource use exist. In contexts where economic dependence on agriculture is stark, these kinds of interventions may help prevent socio-ecological conflicts product of the advancement of the agricultural frontier. Also, SLUS is a promising tool to create food security and coordinate policies around land restitution or illicit crop substitution programs where a conservation approach is compatible with agricultural production around dialogue and horizontal governance.

Supporting information

S1 Data. Workshop’s Data on prioritization of socio-environmental conflicts in Cesar and Caquetá.

https://doi.org/10.1371/journal.pclm.0000075.s001

(XLSX)

Acknowledgments

We acknowledge Miguel Romero and John Jairo Hurtado from the Alliance Bioversity CIAT and their teams that collected the household survey and semi-structured interviews data. Also, Fabio Alexander Castro–Geographer Alliance Bioversity CIAT. Special thanks to the farmers, local experts and farming families who participated in the research activities. An extended acknowledgement to all members of the SLUS project.

This research was partially funded by Agrilac Resiliente and by Mitigate+: Research for Low Emissions Food Systems. We would like to thank all funders who supported this research through their contributions to the CGIAR Trust Fund.” It was also funded by the project 18_III_106_COL_A_Sustainable productive strategies. This project is part of the International Climate Initiative (IKI). The Federal Ministry for the Environment, Nature Conservation and Nuclear Safety (BMU) supports this initiative on the basis of a decision adopted by the German Bundestag. The views expressed in this paper cannot be taken to reflect the official opinions of these organizations.

References

  1. 1. Unruh JD. Land and Post-conflict Peacebuilding. By Jon Unruh and Rhodri Williams.
  2. 2. Unruh J, Williams RC. Land and post-conflict peacebuilding. Land and Post-Conflict Peacebuilding. Taylor and Francis; 2013.
  3. 3. Bruch C, Muffett C, Nichols SS. Natural Resources and Post-Conflict Governance: Building a Sustainable Peace. 2016.
  4. 4. Morales-Muñoz H, Löhr K, Bonatti M, Eufemia L, Sieber S. Assessing impacts of environmental peacebuilding in Caquetá, Colombia: a multistakeholder perspective. Int Aff. 2021;97: 179–199.
  5. 5. Froese R, Schilling J. CLIMATE CHANGE AND CONFLICTS (E GILMORE AND E TENNANT, SECTION EDITORS) The Nexus of Climate Change, Land Use, and Conflicts.
  6. 6. Bonatti M, Medina L, Rodríguez T, del Río M, Morales Muñoz H, Eufemia L, et al. Social learning for designing and scaling out sustainable land-use systems in conflict-affected areas. Policy Brief. 2022.
  7. 7. Castro-Nunez A. Responding to Climate Change in Tropical Countries Emerging from Armed Conflicts: Harnessing Climate Finance, Peacebuilding, and Sustainable Food. Forests. 2018;9: 621.
  8. 8. Nations United. Resolution adopted by the General Assembly on 25 September 2015 70/1. Transforming our world: the 2030 Agenda for Sustainable Development. European Journal of Health Law New York; 2015 pp. 508–516.
  9. 9. UN Security Council. Resolution 2282 (2016) on Review of United Nations Peacebuilding Architecture. In: Resolution A/70/714-S/2016/115 [Internet]. 2016 [cited 6 Jul 2021]. Available: https://www.un.org/press/en/2016/sc12340.doc.htm.
  10. 10. Rüttinger L, Smith D, Stang G, Tänzler D, Vivekananda J. A New Climate for Peace. Berlin; 2015.
  11. 11. Tänzler D, Maas A, Carius A. Climate change adaptation and peace. Wiley Interdiscip Rev Clim Change. 2010;1: 741–750.
  12. 12. Holleman C, Jackson J, Sánchez M V, Vos R. Sowing the seeds of peace for food security: Disentangling the nexus between conflict, food security and peace. Rome; 2017.
  13. 13. GCF. Independent Evaluation of the Green Climate Fund’s Environmental and Social Safeguards (ESS) and the Environmental and Social Management System (ESMS). Incheon, Korea; 2020.
  14. 14. Krampe F, Hegazi F, VanDeveer SD. Sustaining peace through better resource governance: Three potential mechanisms for environmental peacebuilding. World Dev. 2021;144: 105508.
  15. 15. Ide T, Bruch C, Carius A, Conca K, Dabelko GD, Matthew R, et al. The past and future(s) of environmental peacebuilding. Int Aff. 2021;97: 1–16.
  16. 16. Baptiste B, Pinedo-Vasquez M, Gutierrez-Velez VH, Andrade GI, Vieira P, Estupiñán-Suárez LM, et al. Greening peace in Colombia. Nat Ecol Evol. 2017;1: 102. pmid:28812667
  17. 17. Clerici N, Salazar C, Pardo-Díaz C, Jiggins CD, Richardson JE, Linares M. Peace in Colombia is a critical moment for Neotropical connectivity and conservation: Save the northern Andes–Amazon biodiversity bridge. Conserv Lett. 2019;12.
  18. 18. Sylvester J, Valencia J, Verchot LV., Chirinda N, Romero Sanchez MA, Quintero M, et al. A rapid approach for informing the prioritization of degraded agricultural lands for ecological recovery: A case study for Colombia. J Nat Conserv. 2020;58: 125921.
  19. 19. IDEAM, Fundación Natura, PNUD, MADS, DNP, CANCILLERÍA. Tercer Informe Bienal de Actualización de Colombia a la Convención Marco de las Naciones Unidas para el Cambio Climático (CMNUCC). Bogotá, Colombia; 2021.
  20. 20. Unda M, Etter A. Conservation opportunities of the land restitution program areas in the colombian post-conflict period. Sustainability (Switzerland). 2019;11.
  21. 21. Graser M, Bonatti M, Eufemia L, Morales H, Lana M, Löhr K, et al. Peacebuilding in Rural Colombia—A Collective Perception of the Integrated Rural Reform (IRR) in the Department of Caquetá (Amazon). Land (Basel). 2020;9: 36.
  22. 22. Morales-Muñoz H, Bailey A, Löhr K, Caroli G, Villarino E, Lobo Guerrero AMa, et al. Co-benefits through coordination of climate action and peacebuilding: a system dynamics model. Journal of Peacebuilding and Development. 2022;17–3.
  23. 23. Skinner E, Castleden H. Natural Resource Management (NRM) BT—Encyclopedia of Quality of Life and Well-Being Research. In: Michalos AC, editor. Dordrecht: Springer Netherlands; 2014. pp. 4260–4264. https://doi.org/10.1007/978-94-007-0753-5_1913
  24. 24. Bocking S. Visions of nature and society: A history of the ecosystem concept. Alternatives. 1994; 12–18.
  25. 25. Holling CS, Meffe GK. Command and control and the pathology of natural resource management. Conservation biology. 1996;10: 328–337.
  26. 26. Malkowsky C. Capturing Real Impacts: Environmental Peacebuilding Evaluation in the Middle East: Lessons Applicable Worldwide. Student Undergraduate Research E-journal! 2019;5: 1–4.
  27. 27. Nanthikesan S, Uitto JI. Evaluating post‐conflict assistance. Assessing and restoring natural resources in post-conflict peacebuilding. London: Routledge; 2013. pp. 393–412.
  28. 28. Furumo PR, Lambin EF. Scaling up zero-deforestation initiatives through public-private partnerships: A look inside post-conflict Colombia. Global Environmental Change. 2020;62: 102055.
  29. 29. Castro-Nunez A, Mertz O, Quintero M. Propensity of farmers to conserve forest within REDD+ projects in areas affected by armed-conflict. For Policy Econ. 2016;66: 22–30.
  30. 30. Krause T. Reducing deforestation in Colombia while building peace and pursuing business as usual extractivism? J Polit Ecol. 2020;27.
  31. 31. Climate THE, Mechanism S. Climate Finance for Sustaining Peace. 2018.
  32. 32. Comisión para el Esclarecimieto de la Verdad la C y la NR. HAY FUTURO si hay verdad Infore Final Hallazgos y Recomendaciones. Bogotá, Colombia; 2022.
  33. 33. Londoño M, Martínez L. El medio ambiente, otra víctima del conflicto armado colombiano actual. Manizales, Colombia: Universidad de Manizales. 2015.
  34. 34. Valenzuela P, Colombia SCSE-E peacebuilding in post-conflict. Environmental peacebuilding in post-conflict Colombia. Routledge Handbook of Environmental Conflict and Peacebuilding. Routledge; 2018. https://doi.org/10.4324/9781315473772-17
  35. 35. Zúñiga-Upegui P, Arnaiz-Schmitz C, Herrero-Jáuregui C, Smart SM, López-Santiago CA, Schmitz MF. Exploring social-ecological systems in the transition from war to peace: A scenario-based approach to forecasting the post-conflict landscape in a Colombian region. Science of the Total Environment. 2019;695. pmid:31756872
  36. 36. Murillo-Sandoval PJ, Van Dexter K, Van Den Hoek J, Wrathall D, Kennedy R. The end of gunpoint conservation: forest disturbance after the Colombian peace agreement. Environmental Research Letters. 2020;15: 034033.
  37. 37. Vanegas-Cubillos M, Sylvester J, Villarino E, Pérez-Marulanda L, Ganzenmüller R, Löhr K, et al. Forest cover changes and public policy: A literature review for post-conflict Colombia. Land use policy. 2022;114.
  38. 38. Ganzenmüller R, Sylvester JM, Castro-Nunez A. What Peace Means for Deforestation: An Analysis of Local Deforestation Dynamics in Times of Conflict and Peace in Colombia. Front Environ Sci. 2022; 51.
  39. 39. IDEAM. Monitoreo desforestacion -. 2021 [cited 28 Sep 2021]. Available: http://www.siac.gov.co/monitoreodesforestacion.
  40. 40. Witness G. Last line of defence. The industries causing the climate crisis and attacks against land and environmental defenders. 2021.
  41. 41. Eufemia L, Pérez P, Rodriguez T, Lozano C, Bonatti M, Morales H, et al. Governance in post-conflict scenarios: assessing models of community-based governance in the departments of Caquetá and Cesar (Colombia). Territ Politic Gov. 2021; 1–23.
  42. 42. Colombia M de MA y DS. C E S a R 2 0 3 2 Cambio Climático Territorial Del. Bogotá, Colombia; 2016.
  43. 43. Gina P. Cambio climático en Caquetá | PID AMAZONIA. [cited 19 Apr 2021]. Available: https://www.pidamazonia.com/content/cambio-climático-en-caquetá.
  44. 44. Morales-Muñoz H, Jha S, Bonatti M, Alff H, Kurtenbach S, Sieber S. Exploring Connections—Environmental Change, Food Security and Violence as Drivers of Migration—A Critical Review of Research. Sustainability. 2020;12: 5702.
  45. 45. Morales L. PEACE AND ENVIRONMENTAL PROTECTION IN COLOMBIA Proposals for Sustainable Rural Development Peace and Environmental Protection in Colombia: Proposals for Sustainable Rural Development 2. 2017.
  46. 46. Graser M, Bonatti M, Eufemia L, Morales H, Lana M, Löhr K, et al. Peacebuilding in Rural Colombia—A Collective Perception of the Integrated Rural Reform (IRR) in the Department of Caquetá (Amazon). Land (Basel). 2020;9: 36.
  47. 47. Unidad para la Atención y Reparación Integral a las Víctimas. DT CAQUETÁ Y HUILA “REPARAMOS A LAS VÍCTIMAS, AQUÍ COMIENZA LA PAZ.” 2015.
  48. 48. Carolina Meza Jéniier González Ariel Ávila M. Recursos y retos para el postconflicto en la región Huila y Caquetá.
  49. 49. Ulloa A, Coronado S. Extractivismos y posconflicto en Colombia: retos para la paz territorial. Universidad Nacional de Colombia; 2016.
  50. 50. Armenteras D, Schneider L, Dávalos LM. Fires in protected areas reveal unforeseen costs of Colombian peace. Nat Ecol Evol. 2019;3: 20–23. pmid:30478307
  51. 51. Martínez G. Construyendo agenda 21 para el departamento de Putumayo: una construcción colectiva para el desarrollo sostenible de la Amazonia Colombiana. Instituto Amazónico de Investigaciones Científicas" SINCHI"; 2007.
  52. 52. URIBE G. Veníamos con una manotada de ambiciones. Santafé de Bogotá: MISEREOR. 1992.
  53. 53. JC J.G., MC L.M., BG J.A. Enfoque Agroambiental: Una mirada distinta a las intervenciones productivas en la Amazonia. Caquetá y Guaviare. Bogotá, Colombia; 2019.
  54. 54. Pérez Marulanda L, Lavelle P, Rudbeck Jepsen M, Castro-Nunez A, Francesconi W, Camilo K, et al. Farmscape Composition and Livelihood Sustainability in Deforested Landscapes of Colombian Amazonia. Agriculture. 2020;10: 588.
  55. 55. Armenteras D, Rodríguez N, Retana J. Landscape Dynamics in Northwestern Amazonia: An Assessment of Pastures, Fire and Illicit Crops as Drivers of Tropical Deforestation. Fuller DQ, editor. PLoS One. 2013;8: e54310. pmid:23382890
  56. 56. Ramírez AB. Panorama de la agricultura en el Cesar. Boletín El Palmicultor. 2018; 21–23.
  57. 57. Bonet J, Aguilera M. Cincuenta años de la economía del Cesar: De la agroindustria del algodón a la extracción del Carbón. Banco de la Republica de Colombia; 2018.
  58. 58. Instituto Geográfico Agustín Codazzi. Suelos del Cesar no dan para tanto cultivo y ganado. 2020 [cited 2 Jul 2022]. Available: https://igac.gov.co/es/noticias/suelos-del-cesar-no-dan-para-tanto-cultivo-y-ganado.
  59. 59. Moreno T, Medina JL, Fuentes AP, Lopera A. Restitución de Tierras en Colombia: Análisis y estudios de caso. Bogotá, Colombia: Centro de Investigación y Educación Popular. 2016.
  60. 60. Maher D. The pro-business effects of paramilitary terror in Colombia: Appreciating different types of political violence and their economic impacts. Paramilitary Groups and the State under Globalization. 2021; 35–52.
  61. 61. Wesche P. Business actors and land restitution in the Colombian transition from armed conflict. https://doi.org/101080/1364298720201773441. 2020;25: 295–322.
  62. 62. Romero M, Torres D. Drummond, Chiquita y paramilitares: Adaptación y negociación de ventajas en medio del conflicto. La Econ los paramilitares Redes corrupció n, negocios y polıtica Corporación Nuevo Arco Iris, Random House Mondadori, SA. 2011; 149–189.
  63. 63. CENTRO NACIONAL DE MEMORIA HISTÓRICA. Y A LA VIDA POR FIN DAREMOS TODO… Memorias de las y los trabajadores y extrabajadores de la agroindustria de la palma de aceite. Bogotá, Colombia; 2018.
  64. 64. PAX. Civil society under threat. Paramilitary violence. Cesar mining region 2012–2016. Utrecht; 2016.
  65. 65. United Nations Human Rights Council. Report of the United Nations High Commissioner for Human Rights on the situation of human rights in Colombia. New York; 2021.
  66. 66. (IKI) IK. Implementing sustainable land use systems to contribute to forest conservation, climate protection (REDD+) and the peace-building process in Colombia. 2021 [cited 2 Jul 2022]. Available: https://www.international-climate-initiative.com/en/project/umsetzung-nachhaltiger-landnutzungssysteme-fuer-den-erhalt-von-waeldern-den-schutz-des-klimas-redd-und-zur-unterstuetzung-des-friedensprozesses-in-kolumbien-18-iii-106-col-m-sustainable-productiv.
  67. 67. Bonatti M, Del Rio M, Rodriguez T, Morales Muñoz H, Eufemia L, Löhr K, et al. Key factors for effective design and implementation of sustainable land use systems to reduce deforestation and enhance peacebuilding in Colombia. 2021.
  68. 68. Cerda R, Deheuvels O, Calvache D, Niehaus L, Saenz Y, Kent J, et al. Contribution of cocoa agroforestry systems to family income and domestic consumption: looking toward intensification. Agroforestry Systems 2014 88:6. 2014;88: 957–981.
  69. 69. Benjamin T, Burniske G, Croft M, Fenton MC. AN ANALYSIS OF THE SUPPLY CHAIN OF CACAO IN COLOMBIA Cacao supply chain in Colombia View project CLIMATE-SMART AGRICULTURE View project. 2018.
  70. 70. Rodríguez T, Bonatti M, Löhr K, Lana M, Del Río M, Sieber S. Analyzing influencing factors to scale up agroforestry systems in Colombia: A comparative ex-ante assessment of cacao farming and cattle ranching in two regions. Agroforestry Systems. 2022;96: 435–446.
  71. 71. Castro-Nunez A, Charry A, Castro-Llanos F, Sylvester J, Bax V. Reducing deforestation through value chain interventions in countries emerging from conflict: The case of the Colombian cocoa sector. Applied Geography. 2020;123: 102280. https://doi.org/10.1016/j.apgeog.2020.102280.
  72. 72. Cocoa and Forest Initiative. Cocoa, Forests and Peace Initiative in Colombia Joint Framework for Action. Colombia; 2018.
  73. 73. Romero Sanchez MA, Perez Marulanda L, Quintero M, Gonzalez C, Calderon V, Vanegas S, et al. Socioeconomic and environmental survey for implementing sustainable cacao systems for forest conservation for climate change mitigation and peacebuilding in Colombia. The Alliance of Bioversity International and CIAT A4—Federal Ministry for the Environment Building and Nuclear Safety (BMUB) - 18_III_106_COL_M_Sustainable productive strategies NC, editor. Harvard Dataverse;
  74. 74. Löhr K, Aruqaj B, Baumert D, Bonatti M, Brüntrup M, Bunn C, et al. Social Cohesion as the Missing Link between Natural Resource Management and Peacebuilding: Lessons from Cocoa Production in Côte d’Ivoire and Colombia. Sustainability 2021, Vol 13, Page 13002. 2021;13: 13002.
  75. 75. Fouché C, Light G. An Invitation to Dialogue: ‘The World Café’In Social Work Research. Qualitative social work. 2011;10: 28–48.
  76. 76. Löhr K, Weinhardt M, Sieber S. The “World Café” as a participatory method for collecting qualitative data. Int J Qual Methods. 2020;19: 1609406920916976.
  77. 77. Reboratti C. Socio-environmental Conflict in Argentina. Journal of Latin American Geography. 2012;11: 3–20.
  78. 78. Neumann J, Heinrich W, Wustrow K. Do No Harm Trainer’s Manual. 2018.
  79. 79. Wessells MG. Do no harm: toward contextually appropriate psychosocial support in international emergencies. American psychologist. 2009;64: 842. pmid:19899908
  80. 80. Weiss CH. Nothing as practical as good theory: Exploring theory-based evaluation for comprehensive community initiatives for children and families. New approaches to evaluating community initiatives: Concepts, methods, and contexts. 1995;1: 65–92.
  81. 81. Peacebuilding Evaluation Consortium. Guiding Steps for Peacebuilding Design, Monitoring, and Evaluation. 2017. Available: http://cdacollaborative.org/publication/no-harm-workshop-trainers.
  82. 82. Service UFA. Colombia: Cacao for Peace Overview |. 2016 [cited 28 Sep 2021]. Available: https://www.fas.usda.gov/data/colombia-cacao-peace-overview.
  83. 83. Martínez-Salgado C. Sampling in qualitative research: basic principles and some controversies. Cien Saude Colet. 2012;17: 613.
  84. 84. Grimm P. Social Desirability Bias. Wiley International Encyclopedia of Marketing. John Wiley & Sons, Ltd; 2010. https://doi.org/10.1002/9781444316568.wiem02057
  85. 85. Salmanowitz N. The impact of virtual reality on implicit racial bias and mock legal decisions. J Law Biosci. 2018;5: 174–203. pmid:29707220
  86. 86. Canavire-Bacarreza G, Diaz-Gutierrez JE, Hanauer MM. Unintended consequences of conservation: Estimating the impact of protected areas on violence in Colombia. J Environ Econ Manage. 2018;89: 46–70.
  87. 87. Clerici N, Armenteras D, Kareiva P, Botero R, Ramírez-Delgado JP, Forero-Medina G, et al. Deforestation in Colombian protected areas increased during post-conflict periods. Sci Rep. 2020;10. pmid:32188909
  88. 88. Prem M, Saavedra S, Vargas JF. End-of-conflict deforestation: Evidence from Colombia’s peace agreement. World Dev. 2020;129: 104852.
  89. 89. UN Peacebuilding Support Office. What does Sustaining Peace mean? New York; 2017.
  90. 90. Chambers R. From PRA to PLA and Pluralism: Practice and Theory. Development. 2007;IDS WORKIN: 41. IDS Working Paper 286.
  91. 91. Linton S, Clarke A, Tozer L. Strategies and Governance for Implementing Deep Decarbonization Plans at the Local Level. Sustainability. 2020;13: 154.
  92. 92. Emmanuel S, Leonard MS, Richard C, Gladys B. Natural Resource-Based Global Conflicts and Post Conflict Peace Building. IOSR Journal of Environmental Science. 2015;9: 53–61.
  93. 93. Ide T. The dark side of environmental peacebuilding. World Dev. 2020;127: 104777.
  94. 94. Walch C. From curse to blessing–how natural resources affect peace and conflict in the Philippines. Routledge Handbook of Environmental Conflict and Peacebuilding. 2018; 254–264.
  95. 95. Altman SSL, Nichols SS, Woods JT. Leveraging high-value natural resources to restore the rule of law: The role of the Liberia Forest Initiative in Liberia ‘ s transition to stability. … -Value Natural Resources …. 2006;1: 337–366.
  96. 96. Karimi A, Hockings M. A social-ecological approach to land-use conflict to inform regional and conservation planning and management. Landsc Ecol. 2018;33: 691–710.
  97. 97. FAO. PEACE AND FOOD SECURITY Investing in resilience to sustain rural livelihoods amid conflict. 2017;58.
  98. 98. Corps Mercy. Motivations and Empty Promises”: Voices of Former Boko Haram Combatants and Nigerian Youth’. April. New York; 2016. Available: https://www.mercycorps.org/sites/default/files/2019-11/Motivations and Empty Promises_Mercy Corps_Full Report_0.pdf.
  99. 99. Marulanda LP, Lavelle P, Jepsen MR, Castro-Nunez A, Francesconi W, Camilo K, et al. Farmscape composition and livelihood sustainability in deforested landscapes of colombian amazonia. Agriculture (Switzerland). 2020;10: 1–20.
  100. 100. Das MB, Espinoza SA. Socioeconomic Inclusion in International Development. Untapped Power: Leveraging Diversity and Inclusion for Conflict and Development. 2022; 397.
  101. 101. Lind J. Manufacturing peace in “no man’s land”: Livestock and access to natural resources in the Karimojong Cluster of Kenya and Uganda. Livelihoods, natural resources, and post-conflict peacebuilding. 2015.
  102. 102. Galtung J. Conflict transformation by peaceful means: The Transcend method. UN; 1999.
  103. 103. Ropers N. From Resolution to Transformation: The Role of Dialogue Projects. Transforming Ethnopolitical Conflict. 2004. pp. 255–269.
  104. 104. Hendrix CS, Noland M. Confronting the curse: the economics and geopolitics of natural resource governance. Choice Reviews Online. 2014;52: 52-0959-52–0959.
  105. 105. Young H, Goldman L. Livelihoods, natural resources, and post-conflict peacebuilding. Routledge; 2015.
  106. 106. Muller K, Domfeh KA, Yeboah-Assiamah E. Institutional assessment in natural resource governance: A conceptual overview. Forest Policy and Economics. Elsevier B.V.; 2017. pp. 1–12. https://doi.org/10.1016/j.forpol.2016.10.006
  107. 107. Brown K. Integrating conservation and development: A case of institutional misfit. Frontiers in Ecology and the Environment. Ecological Society of America; 2003. pp. 479–487.
  108. 108. Halsall J, Oberoi R, Cooke IG, Wankhade P. Understanding community governance: a global perspective. International Journal of Asian Social Science. 2013;3: 1112–1127.
  109. 109. McGinnis MD, Ostrom E. Social-ecological system framework: Initial changes and continuing challenges. Ecology and Society. 2014;19.
  110. 110. Hoffmann C, García Márquez JR, Krueger T. A local perspective on drivers and measures to slow deforestation in the Andean-Amazonian foothills of Colombia. Land use policy. 2018;77: 379–391.
  111. 111. Froese R, Schilling J. The Nexus of Climate Change, Land Use, and Conflicts. Current Climate Change Reports. Springer; 2019. pp. 24–35. https://doi.org/10.1007/s40641-019-00122-1
  112. 112. McDermott CL, Coad L, Helfgott A, Schroeder H. Operationalizing social safeguards in REDD+: Actors, interests and ideas. Environ Sci Policy. 2012;21: 63–72.
  113. 113. Zúñiga-Upegui P, Arnaiz-Schmitz C, Herrero-Jáuregui C, Smart SM, López-Santiago CA, Schmitz MF. Exploring social-ecological systems in the transition from war to peace: A scenario-based approach to forecasting the post-conflict landscape in a Colombian region. Science of the Total Environment. 2019;695: 133874. pmid:31756872