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Which knowledge matters? Decision-making in conservation and development initiatives

  • Clara Léonie Diebold ,

    Roles Conceptualization, Formal analysis, Investigation, Methodology, Project administration, Visualization, Writing – original draft, Writing – review & editing

    clara.diebold@students.unibe.ch

    Affiliations Wyss Academy for Nature at the University of Bern, Bern, Switzerland, Institute of Geography, University of Bern, Bern, Switzerland, Centre for Development and Environment (CDE), University of Bern, Bern, Switzerland

  • Peter Messerli,

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

    Affiliations Wyss Academy for Nature at the University of Bern, Bern, Switzerland, Institute of Geography, University of Bern, Bern, Switzerland

  • Paul Clément Harimalala,

    Roles Investigation, Methodology, Writing – review & editing

    Affiliation Ecole Supérieur des Sciences Agronomiques, Département des Eaux et Forêts, Université d’Antananarivo, Antananarivo, Madagascar

  • Sarah-Lan Mathez-Stiefel,

    Roles Conceptualization, Methodology, Writing – review & editing

    Affiliations Wyss Academy for Nature at the University of Bern, Bern, Switzerland, Centre for Development and Environment (CDE), University of Bern, Bern, Switzerland

  • Julie Gwendolin Zaehringer

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

    Affiliations Wyss Academy for Nature at the University of Bern, Bern, Switzerland, Institute of Geography, University of Bern, Bern, Switzerland, Centre for Development and Environment (CDE), University of Bern, Bern, Switzerland

Abstract

In regions where local livelihood needs intersect with international conservation priorities, finding ways to safeguard biological diversity while promoting human well-being is essential. Beyond debates on different approaches, the literature highlights critical research gaps regarding governance processes in conservation and development initiatives. This study examines how participation of local actors and inclusion of different knowledges shape decision-making in such initiatives. We introduce a novel analytical lens that combines three complementary frameworks: participation, knowledge sources (local, scientific, and practitioner), and knowledge types (systems, target, and transformation knowledge). By applying this lens to four conservation and development initiatives in Madagascar, we trace how participation and knowledge inclusion evolved over time. Our results show that local participation and the inclusion of diverse knowledge sources generally increased throughout the initiatives’ trajectories. However, participation often remained consultative, creating a risk of extracting local knowledge without granting genuine influence over decisions. The involvement of local actors and the combination of multiple knowledge sources largely depended on deliberate choices by project managers and funders, highlighting both power asymmetries and the agency of those leading these interventions. Analysis through the lens of knowledge types further revealed that insufficient integration of systems, target, and transformation knowledge resulted in significant setbacks in the initiatives’ trajectories, underscoring the importance of intentional knowledge integration in decision-making. Taken together, these findings highlight the central role of knowledge co-production in the design and implementation of conservation and development initiatives. Facilitating iterative co-production processes that explicitly address power relations, engage plural worldviews, and integrate systems, target, and transformation knowledge offers a promising pathway to strengthen the governance of such initiatives. These insights provide practical guidance for informing ongoing and future conservation and development actions.

Author summary

Biodiversity conservation often takes place in areas where people depend directly on natural resources for their livelihoods. In such contexts, conservation measures can negatively affect people’s well-being. Conservation and development initiatives aim to balance this tension, but more attention is needed on how such initiatives are governed and managed.

In this study, we examined decision-making in four conservation and development initiatives in Madagascar. We asked who was involved in key decisions, whose knowledge was taken into account, and which types of knowledge were included. We distinguish between systems knowledge (how things work), target knowledge (defining goals and priorities), and transformation knowledge (how to bring about change). Based on detailed case histories, we traced how participation and knowledge inclusion evolved over time.

Across the four initiatives, local participation increased over time, but often remained limited to consultation. Whether local perspectives shaped decisions or different knowledge sources were combined depended largely on choices made by managers and funders. We also found that initiatives faced setbacks when key types of knowledge were insufficiently considered in decision-making. Overall, our findings highlight the importance of bringing together local communities, practitioners, and researchers to jointly produce knowledge throughout an initiative’s trajectory.

1. Introduction

In regions where poverty is widespread and people’s livelihoods depend on land, conservation measures – such as the establishment of protected areas – often worsen the situation of affected communities [1,2]. Recognition of these tensions has led to the emergence of conservation and development initiatives (CDIs), which seek to conserve biological diversity while promoting human well-being within ecological boundaries [3,4]. Previous research has examined CDIs primarily in terms of their goals and strategies [5,6,7,8]. However, scholars increasingly call for closer attention to procedural and governance aspects, including how decision-making processes are shaped by power dynamics, knowledge, and actors’ values and interests [4,9,10].

Enhancing the role of local communities in environmental decision-making is frequently highlighted as a means of fostering more equitable governance [11]. Beyond ensuring full and effective participation in decision-making, equitable governance entails acknowledging diverse knowledge systems, values, and cultural practices while upholding rights to ancestral lands [12]. The importance of involving local actors in conservation has been acknowledged for more than thirty years [e.g., 13,14,15,16]. Although the impact of participatory approaches remains contested, a growing number of systematic reviews suggests a positive relationship between equitable governance and ecological and social conservation outcomes [17,16,11]. Following Reed [18], we define participation as a process whereby individuals, groups, and organisations actively engage in decision-making on issues that directly impact them. Both normative and pragmatic arguments support the inclusion of diverse actors – particularly local communities – in environmental governance [18,16]. Normative arguments centre on principles of equity as well as epistemic and cognitive justice [see 19]. Pragmatic arguments emphasise the potential for stakeholder engagement to improve the quality and long-term effectiveness of conservation interventions. As participation is inherently shaped by power dynamics [20,21], outcomes of participatory approaches depend on how they are designed and implemented [22,23]. Scholars emphasise the need to include local actors from the earliest stages to ensure they can meaningfully shape key design decisions [18,24,15]. This underscores the importance of examining participation across the entire CDI timeline [25], and of assessing the quality of participatory processes in light of persistent critiques that they often remain at a consultative level and reproduce existing power hierarchies [26,27].

Beyond questions of participation, increasing attention has been paid in recent years to the importance of drawing on Indigenous and local knowledge (ILK) for biodiversity conservation [28,29]. ILK systems are now widely recognised as complementary to scientific approaches – not only for the insights they offer into social-ecological systems, but also for their distinct ways of conceptualising human–nature relationships [30,31,32]. This shift is reflected in efforts to weave multiple knowledge systems into global assessments such as the IPBES report [33,34] and the newly published Global Environmental Outlook 7 [35]. Nevertheless, combining ILK and scientific knowledge in conservation management remains challenging, as it involves navigating fundamental differences in worldviews, values, and practices – often within contexts marked by power asymmetries and unequal recognition [30,36,37,38]. Meanwhile, conservation decisions frequently rely on practitioners’ professional knowledge, with scientific evidence used only marginally [39,40,41]. For example, Giehl et al. [42] found that protected area managers in Brazil based decisions largely on their personal experience, consulting scientific evidence only occasionally. Similarly, a national survey of Canadian protected area managers found that information generated by organisational staff was prioritised over other evidence, including Indigenous knowledge and peer-reviewed literature [43]. This evidence-practice gap has been linked to barriers such as limited accessibility of scientific literature, organisational constraints, and a lack of knowledge co-production processes between researchers and decision-makers [40,44,45,46].

To address complex socio-ecological challenges, sustainability science has long promoted transdisciplinary approaches that foster knowledge co-production across disciplines and societal actors [47]. In addition to the combination of diverse knowledge sources (e.g., local, scientific, and practitioner), scholars have drawn attention to the value of distinguishing between three types of knowledge to orient thinking towards more informed and equitable decision-making [48]. Developed in 1997 by a consortium of Swiss researchers [49], the three types of knowledge encompass understanding of systemic interactions (systems knowledge), the plurality of values and interests in setting goals (target knowledge), and concrete strategies for change (transformation knowledge) [50,51,52]. Separating target knowledge from other knowledge types requires making values and assumptions explicit [cf. 21] and thus facilitates engagement with the normative dimensions of sustainability problems [51,53]. By differentiating these knowledge types, potential solutions can be co-developed with affected actors, supporting a shift from problem analysis towards identifying pathways to sustainable development [52]. So far, the distinction between systems, target, and transformation knowledge has been employed to develop research agendas [54], design transdisciplinary projects [48], identify knowledge gaps [55], and design collective actions [56]. Additionally, several studies have examined how these knowledge types are integrated in transdisciplinary research projects [57,58,59]. However, to our knowledge, this typology has not yet been applied to the design and implementation of CDIs.

By applying the three dimensions of participation, knowledge sources, and knowledge types as an analytical framework, we introduce a novel lens for examining decision-making in CDIs. We analyse how these dimensions manifest and evolve over time, tracing them across the “case biographies” of four CDIs in Northeastern Madagascar to identify common patterns and reflect on implications for CDI design and management. Madagascar embodies longstanding tensions between conservation and local livelihoods [60,61], shaped by colonial and postcolonial power asymmetries including externally driven conservation agendas [62,63,64]. These dynamics make Madagascar a particularly suitable setting for examining how the inclusion or exclusion of diverse actors and their knowledge shape governance processes, and for generating insights to support more context-sensitive, effective, and equitable CDI design and implementation.

2. Methods

2.1. Ethics and positionality statement

2.1.1. Ethics statement.

At the time this research was conceived and initiated, the University of Bern did not have a formal ethics committee in place; however, the study was approved internally by the institutional research panel of the Wyss Academy for Nature. Further, a research permit (No. 137) was obtained from the Directorate of Protected Areas, Renewable Natural Resources and Ecosystems (DAPRNE) within the Ministry of Environment and Sustainable Development of Madagascar. For the research design and implementation, we followed the 11 ethical principles outlined in the guidelines of the Swiss Alliance for Global Research Partnerships [65]. Prior to each interview, we explained the purpose of the study to participants and invited questions. Interviews proceeded only after participants gave oral consent to participate and to be audio recorded. Verbal, rather than written, consent was sought for two main reasons: first, we anticipated that not all participants would be fully literate; second, due to historically negative experiences with signing documents, many people in the study region are hesitant to provide written consent [see 66]. Participants were informed that they could skip any questions or withdraw from the interview at any time. To protect participant anonymity, and due to the risk of identification based on the nature of the interviews – which addressed specific organisational issues – interview transcripts remain confidential and are accessible only to the lead author. Research findings have been shared with participants both in written form and through oral presentations.

2.1.2. Positionality.

The author team has backgrounds in geography, environmental sciences, anthropology and ethnobiology, situated within sustainability science. All authors have extensive field experience in Madagascar. The study’s focus on knowledge inclusion reflects the authors’ previous work on ILK and knowledge types, while the emphasis on participation emerged mainly from the first author’s preliminary observations and regional contextual knowledge.

Interviews were conducted by the first and third authors. The first author is a PhD student from Switzerland who had spent several months in the study region prior to data collection and lived in Maroantsetra while conducting participatory observation with the Full Circle Initiative (FCI). At the time, her understanding of Malagasy was limited. The third author is from Maroantsetra, is widely respected as an elder, and served as a research assistant and local coordinator for FCI, which facilitated access and contextual understanding. To reduce potential bias, interviews with FCI staff were conducted primarily by the first author. Nevertheless, the depth of data on FCI was greater than for the other case study initiatives, which may have slightly weighted findings toward this case.

Data analysis was conducted by the first author. We acknowledge that, given the qualitative nature of the study, findings are shaped by the researcher’s perspective [67]. Biographies reconstructed from interviews may be incomplete, as they reflect both analytical interpretation and the narrative structure of the interviews. To mitigate this, the analysis was triangulated with secondary sources and co-authors were consulted in ambiguous cases. While this may have influenced specific classifications, we are confident that the overall patterns remain robust.

2.2. Analytical framework

To examine decision-making in the four CDI cases, we developed an analytical framework that combines the three dimensions of participation, knowledge sources, and knowledge types. In the following sections, we explain the rationale for selecting these concepts and how we define and apply them in our analysis.

2.2.1. Participation.

While participation has long been discussed in conservation [16], recent literature increasingly emphasises the need to examine how power shapes not only participatory processes but conservation action more broadly [68,21,20]. When we designed this study, we sought to generate insights of practical relevance to the investigated CDIs and comparable interventions globally, hence our focus on participation and knowledge inclusion, which can be directly influenced by CDI managers. Conversely, addressing power asymmetries is more challenging, as these are embedded in broader structural conditions that exceed the agency of individual initiatives. Nonetheless, by analysing who takes decisions throughout the CDI biographies, we seek to shed light on some aspects of actor-centred power [see 21,69].

Numerous typologies have been developed to classify levels of participation, including the “ladder of participation” [70] and the “wheel of participation” [22]. Across these typologies, a consistent distinction is made between actors holding only a consultative role versus real decision-making power. To reflect these typologies while keeping the framework simple enough to combine with the two knowledge frameworks, we distinguish between two categories: “decision-making”, referring to actors who had a formal role in deciding something, and “consultation”, referring to actors who provided input but did not hold final authority in making the decision. Building on debates that emphasise the importance of local participation in CDI decision-making [16] and recognising that authority over conservation in Madagascar typically rests with international and national actors [63,64], we categorised actors involved in decision-making by place of residence: international, national, district, village staff, and local community. “Village staff” refers to village residents employed by the CDIs, as well as those otherwise directly involved, such as members of CDI-affiliated associations or selected beneficiaries. Although those categorised as “village staff” and “local community” often live in the same area, we distinguished between them to differentiate participation by a selected group of individuals from broader processes open to all community members. In our study, we use the term actors to refer broadly to all individuals and groups involved in or affected by decision-making processes, including stakeholders, rights-holders, and knowledge holders. The term stakeholders – defined as persons or groups who have a legitimate interest (“stake”) in the organisation, issue, or process [71] – is used only where it reflects established terminology.

2.2.2. Sources of knowledge: local, scientific, and practitioner.

In line with debates on the complementarity between ILK and scientific knowledge in environmental governance [33,35], and recognising the relevance of practitioner knowledge in conservation management [40], we distinguish between “local”, “scientific”, and “practitioner” knowledge for our analysis [see also 36 for a similar approach]. For local knowledge, we draw on the definition of traditional ecological knowledge as a “cumulative body of knowledge, practice, and belief, evolving by adaptive processes and handed down through generations by cultural transmission, about the relationship of living beings (including humans) with one another and with their environment” [72, 1252]. However, we expand it to include other dimensions of local knowledge beyond the ecological one. While the term traditional knowledge is closely related [73], it may obscure the dynamic nature of ILK, and undermine its validity as a contemporary knowledge system [74]. As Malagasy people do not typically self-identify as Indigenous, we refer to “local knowledge” in this study rather than ILK.

Scientific knowledge is generally understood as knowledge generated through systematic research methods, characterised by its emphasis on repeatability and justification [32,74]. Although frequently perceived as inherently “objective”, it is, like all knowledge systems, socially situated and shaped by underlying values and assumptions [74,32]. To emphasise their roots in Eurocentric paradigms, dominant forms of scientific knowledge are commonly referred to as ‘Western science’ [75,76]. In efforts to combine different knowledge sources, scientific knowledge is often treated as the benchmark against which ILK is validated – an approach that has been widely criticised for reinforcing epistemic hierarchies [75,36,32].

Practitioner knowledge refers to the professional knowledge of conservation practitioners [39,40]. Although it can also be understood as a form of experiential knowledge – that is, knowledge grounded in personal experience [77] – we use the term practitioner knowledge to distinguish it from local residents’ experiential knowledge, which we subsume under “local knowledge”.

Literature often refers to ILK, scientific, and practitioner knowledge as knowledge systems, emphasising culturally and socially embedded and epistemologically distinct ways of knowing [78]. To avoid confusion with the other dimension of our analytical framework that distinguishes systems, target, and transformation knowledge, we instead adopt the term knowledge sources, commonly used in transdisciplinary research [79,80]. While we distinguish these sources for analytical purposes, in practice, all knowledge systems are dynamic, interrelated, and continually shaped through exchange and adaptation [78].

2.2.3. Types of knowledge: systems, target, and transformation.

In contrast to the sources of knowledge, which describe where knowledge stems from, the distinction between systems, target, and transformation knowledge refers to what the knowledge is about. The two dimensions of the framework are thus complementary: each of the three types of knowledge can originate from any of the three sources, or from a combination thereof. Systems knowledge provides descriptive, explanatory understanding of a situation and its dynamics – “What is?”. Target knowledge relates to values and visions for a desired future – “What ought to be?”. Transformation knowledge, sometimes also referred to as operational knowledge [e.g., 56], focuses on how to move from the current state to the envisioned future – “How to?” – by identifying strategies, tools, and pathways for change [49,51,81]. These types of knowledge overlap, meaning that a single decision can be based on multiple knowledge types.

2.3. Research area and case studies

2.3.1. Research area.

This study focuses on CDIs operating in the Maroantsetra district on Madagascar’s east coast. The region’s first major protected area, Masoala National Park (Masoala NP), was established in 1997 as an Integrated Conservation and Development Project (ICDP) [82]. It was followed by the Makira Natural Park in 2005 (officially designated in 2012), implemented as a REDD+ initiative [83]. Both parks are zoned into a strictly protected core, inhabited areas permitting limited subsistence use, and buffer zones where regulated community resource use is allowed. Management of the buffer zones was delegated to local community associations shortly after the parks’ creation; however, these arrangements have been described as poorly adapted to the local context and largely dysfunctional [84,85]. While the impacts of these protected areas on local well-being have been mixed, they have intensified the challenges local communities face in securing their livelihoods, especially among already marginalised households [86]. Beyond its impacts, Masoala NP has been strongly criticised for how it was implemented, particularly its engagement with local communities [66]. Consistent with patterns observed across Madagascar [63], CDIs in Maroantsetra have largely been initiated by external international – and sometimes national – actors. Apart from the protected areas, most initiatives have operated for only three to five years, leading local communities to perceive them as short-lived and inconsistent.

2.3.2. Case studies.

Our study investigates four CDIs: The Full Circle Initiative (FCI); Sehatry ny Mpamokatra Landy Ifotony (SEPALI); Masoala NP; and Fandroakando. They were selected from approximately 15 initiatives operating at the intersection of nature conservation and human well-being in the Maroantsetra district, based on the following criteria:

  1. a. Clear link to forest conservation. Excluded: initiatives focused on other ecosystems or on environmental, social, or economic activities not directly related to forest conservation.
  2. b. Ongoing and operational initiatives. Excluded: concluded, near termination, or minimally active initiatives.

To allow for comparability across cases, we focused exclusively on forest conservation and did not consider other environmental or social initiatives. Criterion b) was important to enable the collection of accurate and up-to-date information and because we planned to collaborate with the case study initiatives in a participatory process beyond the study presented here. While we intended to include both locally designed initiatives and those developed by external actors, no genuinely community-driven initiative that met the selection criteria could be found in the district of Maroantsetra.

The balance between conservation and human well-being objectives varies among the four CDIs. Masoala NP and Fandroakando are area-based conservation initiatives that prioritise conservation while incorporating human well-being goals. In contrast, FCI and SEPALI place an equal emphasis on both objectives. FCI follows a co-design approach to develop systemic interventions, whereas SEPALI focuses on creating nature-positive value chains (see S1 Table for more details).

2.4. Data collection

Data collection was inspired by the innovation biographies approach [87,88], which analyses innovation as a spatially embedded, knowledge-intensive learning process that emerges through interactions among diverse actors [cf. 89]. Methodologically, the approach reconstructs the “biography” of an innovation through narrative interviews, tracing how it evolves over time, across contexts, and through changing actor constellations [87]. While we did not conceptualise CDIs as innovations, we drew on this approach because it provides a process-oriented lens to examine how initiatives develop through actor interactions and knowledge dynamics. Like innovation processes, CDIs unfold over time and are shaped by how knowledge is mobilised and applied. Reconstructing the “biographies” of the CDIs therefore enabled us to trace their developmental trajectories and analyse how participation in decision-making, as well as the inclusion of different knowledge sources and types, evolved throughout each initiative.

For each case, we conducted interviews with CDI leaders and staff across organisational levels, including members of the initiatives’ board or steering committee, office staff based in Maroantsetra, and field agents working in the villages. Where applicable, we interviewed additional actors involved, such as beneficiaries and members of stakeholder platforms. In part one of the interviews, we asked openly about the development and main changes along the timeline of the CDI. In part two, we added structured questions on decision-making processes within the CDI, and inclusion of scientific and local knowledge. S2 Table provides an overview of interviewee characteristics, and S1 File the full interview guidelines, including questions not used for this article.

Between May 2023 and December 2024, we conducted 14–28 interviews per case and 74 interviews in total. Interviews were held in Malagasy, French, English, or Swiss German, depending on interviewee preferences and language skills. Most occurred at interviewees’ workplaces, with a few conducted online. They lasted 15–110 minutes, depending on interviewees’ level of involvement in the respective CDI. Audio recordings were transcribed, and interviews in Malagasy were additionally translated into French. To fill data gaps, we complemented the initial interview data with secondary data, literature, and follow-up interviews.

2.6. Data analysis

We analysed the data through a qualitative content analysis approach [90]. First, using MaxQDA [91], we extracted relevant parts of the interview transcripts by coding them into three main categories: “participation”, “knowledge inclusion”, and “CDI development”. From these categories, we transferred all references to decision-making in an Excel table (see S3 Table). These included, for example, the choice of the CDI’s overall approach, the selection of intervention villages, decisions to change or expand the approach, as well as day-to-day management decisions mentioned by interviewees. For each decision, we recorded who was involved – distinguishing between actors who directly participated in decision-making versus those who were only consulted or contributed inputs. We then ordered the decisions chronologically, using secondary data where necessary, and consolidated them into 13–15 key decisions for each case. Key decisions therefore encompass several related smaller decisions; for example, in the FCI case, multiple adjustments during implementation mentioned separately by interviewees were clustered into the key decision “adaptations in the process”.

To structure the CDI biographies, we grouped key decisions into four functional phases: (1) design, (2) implementation, (3) adaptation, and (4) operation. Though arranged chronologically, we defined the phases more by their function than by their timing. For example, adaptation decisions – aimed at revising the original strategy – sometimes occurred years or even decades apart, but were grouped together according to their shared purpose. We defined design and adaptation decisions as those decisions that shaped the overall direction of the CDI. In contrast, implementation and operation decisions concern how the strategy was carried out: implementation refers to the initial application of the original design, whereas operation refers to ongoing application of the strategy after adaptations.

To analyse knowledge use, we applied the two dimensions of our analytical framework “sources of knowledge” (i.e., local, scientific, practitioner), and “types of knowledge” (i.e., systems, target, transformation) presented in section 2.2. We revisited all instances of knowledge inclusion in MaxQDA, categorised them by source and type, and linked them to corresponding decisions (see S4 Table). During this process, we encountered cases where decision-making was shaped by knowledge that did not fit into the three defined sources. To capture this, we added a fourth category – “other knowledge” – mainly encompassing target knowledge from global discourses, debates, participation in international knowledge fora, etc.

3. Results

We present the summarised biographies of the four CDIs, organised around key decisions (numbered in the text) from initial project design to operations at the time of data collection. Fig 1 provides an overview of these decisions and the participation of different actor groups in decision-making, while Fig 2 illustrates the sources and types of knowledge involved. Full case biographies are provided in S2 File.

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Fig 1. Participation of different actors in key decisions across the trajectories of four Conservation and Development Initiatives (CDIs): Full Circle Initiative (FCI), SEPALI, Masoala National Park (Masoala NP), and Fandroakando.

Key decisions for each CDI are numbered and organised into four phases: design, implementation, adaptation, and operation. Coloured symbols indicate actor groups involved in decision-making; symbols in brackets represent actors who were consulted or provided input but did not hold final authority in making the decision.

https://doi.org/10.1371/journal.pstr.0000248.g001

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Fig 2. Inclusion of different knowledge sources (scientific, local, practitioner, and other) and knowledge types (systems, target, transformation) in decision-making across the trajectories of four Conservation and Development Initiatives (CDIs): (A) Full Circle Initiative (FCI), (B) SEPALI, (C) Masoala National Park (Masoala NP), and (D) Fandroakando.

For each CDI, one diagram is shown per phase – design, implementation, adaptation, and operation. Numbers correspond to the key decisions for each CDI presented in Fig 1.

https://doi.org/10.1371/journal.pstr.0000248.g002

3.1. Full Circle Initiative (FCI)

FCI was founded in 2019 (1) by Swiss actors drawing on prior research activities in North-eastern Madagascar. With participation from a Malagasy researcher, the initiative was designed around two principles: promoting innovative, non-forest-dependent livelihoods (2) and local ownership (3). These design decisions were primarily based on scientific and practitioner systems and target knowledge. During implementation, local participation and the use of local knowledge increased. Village residents proposed livelihood projects, which were selected (4) by the project team and a district-level stakeholder platform based on predefined criteria. Local project owners led implementation (5) with guidance from the project team and external experts. Following a pilot phase, the process was adapted (6) using feedback from local, district, and national actors. FCI also facilitated village visioning workshops (7). Overall, this phase relied mainly on local and practitioner target and transformation knowledge.

In 2022, FCI reached a turning point, when most of the individual projects of local residents were considered unsuccessful. Although projects were locally proposed and technically supported, they often insufficiently considered relevant systems knowledge. For example, a vegetable garden was established near a riverbed but was later destroyed during a cyclone, leading to project abandonment and frustration for the project owner. This outcome might have been avoided had flood risk and cyclone frequency been considered.

That same year, FCI was integrated into the Wyss Academy for Nature (8), a global research-action centre, and shifted its aim towards systems transformation (9). The initiative now explicitly aimed to combine local and external knowledge (10) and added a focus on value chain development (11) and a digital knowledge platform (12). As in the design phase, key decisions were mainly taken by the Swiss-Malagasy steering committee, but now in consultation with the district team, and were informed by scientific and practitioner knowledge across all three knowledge types.

To operationalise the adapted strategy, a shared valley-wide vision (13) was co-developed with local communities and district actors, including inputs from national and international researchers. Future interventions were selected (14) based on an analysis of system levers and the village- and valley-level visions. Operational authority (15) was increasingly transferred to the Malagasy project coordinator. Overall, in this phase, the three knowledge sources and types became more evenly represented.

3.2. SEPALI

SEPALI’s parent organisation, CPALI (Conservation through Poverty Alleviation International), was founded in 2002 by a US entomologist (1). After initial research, silkworm rearing (2) was identified as a promising approach to achieve CPALI’s goals. Although SEPALI’s current director brought expertise on butterfly species from other regions, the team relied heavily on local farmers’ knowledge to identify suitable silk-producing species and host plants (3).

The programme was introduced in villages (4) around the Makira protected area, where silkworm rearing was initially unfamiliar and met with fear. Implementation drew on the Malagasy team member’s community engagement expertise and scientific knowledge, including research to dispel concerns about crop damage. Village selection was initially guided by collaboration with the Wildlife Conservation Society, but growing interest led residents to request the programme. After forming farmer associations, activities began with tree-planting (5). While the Maroantsetra-based team made key decisions, local members contributed implementation knowledge and, following training, associations independently managed village-level activities (6). SEPALI simultaneously secured buyers, set cocoon prices, and registered as a company in Madagascar (7).

When the initial buyer of the raw silk withdrew, SEPALI shifted to producing artisanal silk products (8), first with women in the villages and later through establishing a manufacturing workshop in Maroantsetra. The Malagasy team received product design training from a US expert. Despite some sales, the organisation remained donor-dependent. The 2014 rosewood crisis made securing conservation-related funding difficult. In response, CPALI successfully applied for funding for an insect-for-food programme (9), which drew on local and scientific knowledge, but was discontinued after the funding period due to low farmer interest. Meanwhile, silk production continued, but fluctuations in vanilla and clove prices reduced farmer participation, prompting SEPALI to collaborate with farmers in other regions to stabilise supply (10).

At the time of data collection, product design decisions (11) were led by artisans in Maroantsetra with input from international collaborators, and most sales (12) occurred through CPALI’s wholesale brand, Tanana Silk. Under a purchase guarantee agreement, CPALI covered salaries and managed sales risk, while SEPALI supplied products. Although sales covered most costs, both organisations continued seeking external funding for further development (13). In both the adaptation and operation phases, key decisions were taken at the international and district levels, without local-level consultation. Nevertheless, local knowledge remained present throughout all phases.

3.3. Masoala National Park (Masoala NP)

Masoala NP was established as an ICDP (1) in collaboration between international conservation organisations, the National Association for the Management of Protected Areas (ANGAP), and Madagascar’s Ministry of Forests. Park boundaries (2) were defined based on extensive ecological and socio-economic studies and participatory mapping of village territories [82]. Although communities agreed with the initial design, conflict potential existed from the outset, notably regarding cultivated land, settlement relocation, and cultural values attached to forests [92,66]. The ICDP framework included plans to provide sustainable livelihoods alongside conservation measures (3).

Following the park’s establishment, some livelihood support activities were introduced (4), such as training in intensified rice cultivation, with interventions selected by park management and technical experts. Consistent with national policy, forest management rights in buffer zones were transferred to local communities (5) through VOI (Vondron’Olona Ifotony) associations. While communities were not involved in the decision on the management transfer, they participated in drafting the VOI regulations.

Soon after the park’s creation, declines in global support for ICDPs led to budget cuts and a shift towards strict conservation (6) [93]. Park boundaries were redrawn multiple times (7), moving closer to villages – actions perceived by authorities as technical corrections but by communities as breaches of agreement [66]. Combined with the withdrawal of development support, these changes intensified conflicts [66,93]. More recently, renewed emphasis on participatory conservation led Madagascar National Parks to establish advisory committees (8). In Masoala, the committee included local authorities, government agencies, and other district actors, and, until 2019, evaluated community development proposals (10). The latest five-year management plan (9), renewed in 2023, was developed through a participatory process and additionally informed by scientific knowledge including ecological monitoring and other SMART data.

Based on the management plan, annual planning (11) is developed under the park director’s leadership with staff input and headquarters’ approval. SMART data, alongside staff observations and experience, guide decision-making. While the director retains management authority, staff may propose initiatives, and routine operational decisions such as patrol organisation (12) are taken independently by office and village staff.

3.4. Fandroakando

Fandroakando was founded in 2020 (1) by two Canadian tourists in collaboration with a guide from Maroantsetra, motivated by concerns over forest conservation and the endangered Farankaraina forest. Although the forest was already classified and managed by local VOI associations, limited resources constrained effective management. Following its establishment, Fandroakando collaborated with the VOI while also launching its own initiatives. The founders defined the NGO’s main activities, including patrols, reforestation, and an ecolodge (2). Design-phase decisions were primarily guided by practitioner target and systems knowledge, while scientific knowledge was incorporated through a species inventory conducted prior to the NGO’s creation, and local target knowledge through the establishment of an environmental club (3) proposed by local students.

For implementation of the NGO, the founders secured funding (4), set up operational procedures (5), and created a website, while on-site administration (6), including staff recruitment, was managed by the local guide as executive director. Communication during this period was constrained, particularly due to Covid-19 restrictions, which may partly explain the overall limited use of knowledge in decision-making during the implementation phase. At that time, Fandroakando encountered several implementation challenges, including difficulties in collaborating with the VOI and other conservation actors, and unclear roles and responsibilities within the team.

In early 2023, fraud prompted the dismissal of several staff members and the appointment of a new executive director, followed by the recruitment of additional staff and the formation of a new board (7). The founders, executive director, and board jointly developed the NGO’s first comprehensive strategy (8), informed by staff feedback and community consultations. Based on these inputs, and followed-up by a household survey, a key decision was to place greater emphasis on community development (9). An additional strategic shift involved increased collaboration with other conservation NGOs (10).

At the time of data collection, the founders played a more active role in major management decisions (11), alongside the executive director. Operational changes, including monthly meetings with VOI associations, had improved collaboration and conflict resolution. Office staff implemented activities with the VOI (12), incorporating input from founders, village staff, and other community members, who could also propose development projects (13). Routine decisions (14) were handled by office staff and field agents, and, in addition to practitioner knowledge, were informed by data collected during patrols.

4. Discussion

4.1. Patterns of actor participation and knowledge inclusion in decision-making

We compare the four CDIs across the three dimensions of participation, knowledge sources, and knowledge types, highlighting key patterns and notable differences, and situate them within the broader literature.

4.1.1. Participation.

In three of the four CDIs, initial project design was largely driven by external actors at the international or national level. Fandroakando was a partial exception, involving a district-level actor from the outset. While Masoala NP and Fandroakando included some local input – such as community consultations on land tenure and park boundaries for Masoala NP, and creation of a student-led environmental club for Fandroakando – local actors were not part of the actual decision-making. SEPALI and FCI did not involve local actors at all in the design phase. This pattern is not unique to the cases studied, but has been documented across Madagascar [94,64] and other Global South contexts [e.g., 25,95]. Literature on participation confirms that while early involvement of actors is widely acknowledged as a key principle for successful participatory processes [24], in practice, actors are often engaged only after projects are already designed [18].

Nonetheless, in the four CDIs examined, participation increased significantly in later stages. For instance, during the adaptation phase, in Fandroakando, local actors were consulted for the definition of the organisational strategy. In the case of FCI, the original design and subsequent strategic decisions were made by external actors; however, the design itself incorporated the aim of enabling local communities’ knowledge and visions to inform future decisions. This is reflected in the pattern of participation in decision-making during implementation and operation, where all actor levels were present. In some cases, local actors held key decision-making roles – for instance, defining their community’s vision for 2030, which became a foundation for subsequent planning and action within FCI. The increase of the role of local actors in decision-making at later project stages has been observed in other cases [25] and aligns with Hastings [96], who highlights that implementation-stage decisions by programme managers can still significantly influence local participation and conservation outcomes.

4.1.2. Knowledge sources.

For SEPALI and Masoala NP, all three knowledge sources – local, scientific, and practitioner – contributed to key decisions across all four phases of the CDI timeline. In Masoala NP, decisions were also shaped by other knowledge sources, such as global conservation discourses. In Fandroakando, the implementation phase was an exception, as only practitioner knowledge was present. In FCI, project design and adaptation relied on scientific and practitioner knowledge, but scientific knowledge no longer informed implementation. In the operation phase, however, all three knowledge sources were included. The literature on knowledge use in conservation management highlights a persistent gap between evidence and practice [40,97]. Empirical studies show that most conservation decisions are based on experience-based information and personal judgement of conservation managers rather than scientific evidence [e.g., 41,98,42] or Indigenous knowledge [43]. While practitioner knowledge also played a central role in our cases, the frequent presence of both scientific and local knowledge contrasts with these patterns. Although this may partly reflect questionnaire design, the characteristics of the CDIs also provides an explanation: for example, both FCI and SEPALI were developed by researchers and in FCI, moreover, the valorisation of local knowledge and later the deliberate combination of different knowledge sources were explicit goals of the initiative.

Increasing the participation of local communities in decision-making is widely promoted as a way to include local knowledge and foster more equitable governance [16]. One can therefore assume that the inclusion of local knowledge in the four examined CDIs reflects participation of local actors in the respective decisions. While this assumption was generally supported by our results, a notable exception was SEPALI, where local knowledge – such as knowledge on local butterfly species and their habitats – informed certain design and adaptation decisions despite the absence of local participation. More broadly – and similar to cases observed elsewhere [e.g., 25] – local actors were often only involved in a consultative role, highlighting that knowledge inclusion does not always imply meaningful decision-making influence. This is crucial, as it can result in a one-way process of knowledge extraction and application that is misaligned with local values and priorities [78,99]. The case of Masoala NP illustrates how funders and international actors can override local perspectives, even after initial consultations with local communities. Due to power asymmetries, external priorities may reshape a CDI’s trajectory, undermining earlier agreements. This echoes what Crosman et al. [100] describe as the complex accountabilities of conservation NGOs, where institutional structures and external pressures lead organisations to prioritise funder expectations over commitments made to local communities. Experts suggest that genuine devolution of power to local actors is needed to avoid situations in which external actors override prior agreements [16,11].

Beyond the general question of inclusion, scholars have highlighted the value of combining multiple knowledge sources, such as ILK and scientific knowledge, for more robust, just, and context-relevant decisions [101,32]. Importantly, rather than integrating knowledge into a dominant framework, this should entail weaving different knowledge sources together as components with equal validity [78,36,102]. In our study cases, while local, scientific, and practitioner knowledge were commonly present, they were often used separately rather than in combination. However, a few cases stand out for including all three sources of knowledge. In FCI, key decisions in the operation phase – including the valley vision, selection of major interventions, and on-site activities – intentionally drew on all sources. Masoala NP and Fandroakando combined them in the development of new strategies, whereas SEPALI incorporated them into its ongoing programme development. For FCI, Masoala NP, and Fandroakando, this integration was the result of deliberate choices by the CDIs to foster knowledge combination as a strategic approach.

4.1.3. Knowledge types.

Examining knowledge inclusion through the lens of systems, target, and transformation knowledge, three of the four CDIs showed a progression from limited to broader inclusion of the three knowledge types over time. Some systems knowledge – such as about local land use and livelihoods in FCI and Masoala NP, or about local species in SEPALI and Fandroakando – was used in the design of all CDIs. However, during the implementation phase, FCI and Fandroakando did not draw on systems knowledge for key decisions. In FCI, this was evident in the selection and implementation of individual projects, and likely the main reason many of these locally proposed projects failed, such as the vegetable garden that had to be abandoned due to a lack of attention to environmental conditions. In Fandroakando, the decision on core activities was shaped by a general notion of what a conservation organisation should do, rather than by systematic knowledge use. During implementation, only transformation knowledge was present, and interviewees criticised, for example, a lack of monitoring of activities and their impact on the system. Overall, insufficient consideration of certain knowledge types in early project phases arguably contributed to major setbacks in both CDIs. Both subsequently adapted their strategies, and by the time of data collection, integrated all three knowledge types.

Sustainability science emphasises the importance of jointly developing target knowledge with affected actors, deliberating values and norms [53,57,59]. In line with this, FCI focused on co-creating target knowledge, such as village and valley visions, with local communities, diverse district level actors, including conservation and development practitioners, and external researchers. These visions were then used to guide subsequent activities. In contrast, SEPALI’s objective was set early by international actors and remained unquestioned. While the effect of the fixed objective remains unclear, SEPALI involved little local participation in later phases, possibly contributing to misalignment with local realities, including declining interest due to fluctuating crop prices. Instead of adapting its strategy, SEPALI responded by relocating silk production.

Except for SEPALI, which chose silkworm-rearing as a strategy based on systems and transformation knowledge, the other CDIs did not use transformation knowledge in key design decisions. During implementation, however, all CDIs relied on transformation knowledge, such as technical expertise for establishing alternative livelihood activities in FCI and Masoala NP. While this aligns with literature highlighting the role of transformation knowledge during implementation [48,103,59], its broader use in strategic adaptations within our CDIs points to the value of explicitly considering how goals can best be achieved already during strategy development. Research indicates that local transformation knowledge is often overlooked [104], and that science still lacks comprehensive insights into effective levers for sustainability transformations [52]. In our cases, transformation knowledge emerged from scientific, practitioner, and local knowledge sources but often remained limited to small decisions, such as activity planning. FCI stands out for going further by co-creating knowledge on potential systemic levers. Such approaches [e.g., 105,106] may offer a way forward for better integrating transformation knowledge in CDI decision-making while drawing on diverse knowledge sources.

4.2. Key insights for the design and management of CDIs

Both actor participation and the inclusion or exclusion of knowledge sources are shaped by asymmetrical power structures [21,20]. As illustrated by our cases, in externally initiated and funded CDIs, ultimate authority over initiative design – including whether decision-making power is devolved to local actors – typically rests with founders and funding bodies [107,4]. Although our data do not allow for a systematic assessment of why local communities or their knowledge were only marginally involved in certain phases, existing literature suggests that structural and institutional constraints – including tight design timelines, budget limitations, and fixed donor agendas – play a major role [25,96]. By contrast, SEPALI and Fandroakando emerged from the ideas of a few individuals and evolved without a formal strategy. In these cases, observed patterns – such as the inclusion of local knowledge but not local knowledge holders in SEPALI – appeared to stem less from structural constraints than from limited reflection on the importance of such inclusion. Decisions to involve local actors in decision-making or to combine diverse knowledge sources were, in most instances, the result of explicit choices by those in positions of authority. This underscores the asymmetrical power relations participation and knowledge inclusion are embedded in, while also reflecting the agency of CDI managers and funders in influencing these dynamics [21,4].

While early and comprehensive inclusion of local communities and diverse knowledge systems would be ideal, our cases, and other studies [96], demonstrate that externally designed CDIs can still evolve into more inclusive configurations over time. Our findings suggest that the implications of externally driven design processes depend on whether early decisions result in fixed parameters, such as the spatial boundaries of a protected area, or in adaptive approaches, as is more common in non-area-based CDIs. An additional question, however, is whether externally designed CDIs are open to fundamentally different worldviews and values [see 108,78]. In Madagascar, for instance, the externally introduced concept of “environment” (tontolo iainana) – distinct from land (tany) – has been criticised for contradicting traditional Malagasy understandings of human–nature relationships and dismissing local epistemologies [109,66]. Fully valuing local knowledge therefore requires not only inclusive procedures, but also openness to plural ontologies and the willingness to adapt core conceptual foundations accordingly [110].

At the same time, FCI’s experience demonstrates that valuing local knowledge and devolving decision-making power, while important, is not enough if relevant knowledge types are not adequately considered. The discontinuation of locally proposed projects, due to insufficient attention to systems knowledge, ultimately undermined FCI’s objective of fostering local ownership. Overall, among the three analytical frameworks – participation, knowledge sources, and knowledge types – the framework of knowledge types proved most effective in explaining major setbacks observed in the CDI biographies. Literature highlights that the relative emphasis of systems, target, and transformation knowledge may shift across phases [48,111]. Our findings align with calls for early deliberation of target knowledge with affected actors [103,48] and further indicate that integrating transformation knowledge already during the design phase – by drawing on evidence about effective intervention strategies and inclusive co-design – may enhance strategic robustness and reduce the need for redesign. At the same time, systems knowledge remains critical during implementation, as context-specific knowledge needs may only emerge at that stage. Overall, our results support arguments for the iterative integration of all three knowledge types throughout an initiative’s trajectory [58,103,48].

While our study demonstrates the analytical value of distinguishing between participation, knowledge sources, and knowledge types, practical recommendations converge around processes of knowledge co-production. Rather than limiting co-production to a specific phase, it should be embedded iteratively across all phases — from agenda-setting and CDI design to implementation, evaluation, and adaptation. To strengthen co-design and co-production of knowledge before the launch of an initiative, scholars propose introducing a “Phase 0”, that is, an intentional preparatory period [112]. Although originally discussed for transdisciplinary research projects, its core elements – developing a deep contextual understanding (including local perceptions, expectations, power relations, and existing conflicts) and building trust and shared intent – are equally relevant for CDIs. Additional promising approaches include co-producing a theory of change [113], participatory drafting of management plans [114], and designing co-production processes that engage rather than suppress tensions and power dynamics, for instance through “co-productive agility” [115]. Drawing on the framework of systems, target, and transformation knowledge, Seiferth et al. [56] further demonstrate how these knowledge types can be co-produced through stepwise, dialogue-based workshops. Together, these approaches provide practical entry points for embedding iterative, inclusive knowledge co-production throughout CDI design and implementation.

4.3. Limitations and outlook

By tracing participation, knowledge sources, and knowledge types across the biographies of four CDIs, this study sheds light on how these dimensions interact over time. However, the depth of the data did not allow for an assessment of the quality of participation and knowledge inclusion. For example, even if local visions are considered, it remains unclear whether they genuinely reflect people’s aspirations or are shaped by assumptions about what external actors want to hear. Similarly, while we observed efforts to combine different knowledge sources, we could not determine whether these resulted in equitable collaborations [78,99]. Future research should thus explore these procedural aspects in greater depth. Additionally, examining CDI trajectories using a power-oriented analytical approach could deepen understanding of the dynamics at play, including the reasons behind the in- or exclusion of certain actors and knowledge sources [21,20].

As noted in the introduction, all knowledge systems are continually shaped through exchange and adaptation [78]. Thus, what we call “local knowledge” might not be purely local, but rather shaped through interactions with external influences. In FCI, for example, it was observed that ideas brought forward by local community members were often similar to activities that had been introduced by previous CDIs. In order to advance scientific debates and CDI practice, it may be necessary to pay greater attention to the discourses that shape knowledge [e.g., 116]; the underlying assumptions of local communities, practitioners, and researchers [e.g., 117]; and the question of how to achieve emancipation from decades of external dominance.

5. Conclusion

In this study we examined decision-making in CDIs through the lenses of participation, knowledge sources, and knowledge types. While all study cases were externally initiated, local participation and knowledge inclusion generally increased over time. Participation of local actors, however, often remained consultative, creating a risk of extracting local knowledge without granting genuine influence over decisions. Likewise, whether local actors were involved in decision-making or whether diverse knowledge sources were combined depended largely on explicit choices by those in positions of authority. This underscores the asymmetrical power relations in which participation and knowledge inclusion are embedded, while also highlighting the agency of CDI managers and funders in influencing these dynamics.

Applying the framework of knowledge types, we found that insufficient integration of systems, target, and transformation knowledge – particularly in early phases – contributed to major setbacks in CDI trajectories. Attention to these knowledge types may therefore contribute to more robust decisions and minimise the need for redesign. Taken together, our three analytical lenses point to the central importance of knowledge co-production among CDI staff, local communities, and researchers across different phases, starting ideally even before agenda-setting and including implementation, evaluation, and adaptation. Designing intentional and iterative co-production processes that explicitly address power asymmetries, engage plural worldviews, and systematically integrate systems, target, and transformation knowledge offers a promising pathway for strengthening both ongoing and future CDIs.

Supporting information

S1 Table. Overview of the four Conservation and Development Initiatives (CDIs).

Main characteristics of the four investigated conservation and development initiatives. All data as of April 2025.

https://doi.org/10.1371/journal.pstr.0000248.s001

(DOCX)

S2 Table. Overview of interview respondents.

Numbers of interview respondents categorised by gender, place of residence, and role within the conservation and development initiative (CDI).

https://doi.org/10.1371/journal.pstr.0000248.s002

(DOCX)

S3 Table. Analysis of key decisions in CDI cases.

The table shows key decisions consolidated from smaller decisions, the actors involved in each decision, the assignment of decisions to four phases (design, implementation, adaptation, operation), and the corresponding interview sources.

https://doi.org/10.1371/journal.pstr.0000248.s003

(XLSX)

S4 Table. Analysis of knowledge inclusion in key decisions of the CDI cases.

The table shows instances of knowledge use in key decisions, categorised by source and type, with links to the corresponding key decisions and the respective interview sources.

https://doi.org/10.1371/journal.pstr.0000248.s004

(XLSX)

S1 File. Interview guidelines.

Interview guide used for the interviews with CDI staff, and CDI beneficiaries and other involved actors, respectively. The guideline contains additional questions that were not used for this article.

https://doi.org/10.1371/journal.pstr.0000248.s005

(DOCX)

S2 File. Full Case Biographies.

Complete text of the four CDI case biographies presented in section 3.

https://doi.org/10.1371/journal.pstr.0000248.s006

(DOCX)

Acknowledgments

We would like to wholeheartedly thank all the interview participants who made this study possible. C.L.D. would furthermore like to thank the whole FCI Team in Madagascar for their warm welcome and continuous support. Namely, Paul C. Harimalala and his wife Denise, as well as Melarcia Ravaoarilisy for giving me a home and family in Maroantsetra and ensuring my well-being throughout my stay. Big thanks also go to Tida Tsilanizara for the friendship and the Betsimisaraka lessons, and last but not least to R. Ntsiva N. Andriatsitohaina for the full support in all organisational manners, as well as the willingness to take me along on the FCI’s missions. We profoundly appreciate the work of L. Nancy Rabenantoandro, Lysse Rakotonirainy, and Hyasheille Ramarison in transcribing and translating the Malagasy interview recordings, and the language editing done by Anu Lannen and Madlaina Michelotti. This study contributes to the Global Land Programme (https://glp.earth).

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