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Review

Community Forest Management and REDD+: Pathways to Effective Implementation, Livelihood Improvement, and Climate Change Adaptation in Cambodia

School of Agriculture and Environment, College of Sciences, Massey University, Palmerston North 4414, New Zealand
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Author to whom correspondence should be addressed.
Land 2025, 14(5), 1122; https://doi.org/10.3390/land14051122
Submission received: 21 March 2025 / Revised: 5 May 2025 / Accepted: 13 May 2025 / Published: 21 May 2025

Abstract

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Community Forest Management (CFM) and REDD+ projects have emerged as key strategies for promoting environmental conservation and livelihood improvement. This review explores the effectiveness of incorporating free, prior, and informed consent (FPIC), safeguard principles, grievance redress mechanisms, and benefit-sharing mechanisms into CFM and REDD+ in Cambodia, with a focus on enhancing communities’ livelihoods and climate change adaptation. This paper synthesizes findings from recent literature on CFM and REDD+ in Cambodia and internationally, analyzing key case studies, policy frameworks, and community engagement strategies. Findings suggest that while REDD+ projects offer potential economic and ecological benefits, challenges related to land tenure, equity in benefit-sharing, and community participation remain. This review highlights the need for stronger community engagement, a robust conflict management structure, clear land tenure policies, equitable benefit-sharing mechanisms, and more climate change adaptation activities to ensure the success of CFM and REDD+ projects in Cambodia and the Global South.

1. Introduction

Reducing Emissions from Deforestation and Forest Degradation (REDD+) is a critical program that not only contributes to reducing deforestation and forest degradation rates but also promotes sustainable forest management, forest resource conservation, and carbon storage enrichment [1]. Through this initiative, developing countries are eligible to receive results-based payments for reducing emissions associated with deforestation and forest degradation [2]. A growing body of literature documents many benefits associated with REDD+ projects, including increased stakeholder participation [3,4], improved community livelihoods [5,6,7], strengthened monitoring capacity [8,9], improved forest governance [10], and the protection of indigenous and community land rights [11,12,13].
Globally, deforestation and forest degradation contribute approximately 15% of all anthropogenic greenhouse gas emissions and, as such, are a key driver of climate change [14], contributing to biodiversity loss, increasing soil erosion, and negatively impacting the livelihoods of local communities [15,16]. REDD+ is seen as one effective mechanism that contributes to addressing these issues. Since 2013, 60 countries from the Global South, covering about 1.35 billion hectares, equivalent to 62% of forest areas, have submitted reports to the UN Climate Change Secretariat regarding activities to reduce deforestation and forest degradation [17]. Among these countries, 17 contributed to reducing 11.6 billion tons of carbon dioxide. Specifically, according to its first Biennial Update Report, Cambodia was responsible for reducing emissions by 46,337,172 tons of CO2 in 2018 through the REDD+ program [18]. This represents an important contribution to achieving Cambodia’s targets under the 2015 United Nations Paris Climate Agreement, which aims to limit the global average temperature increase to 1.5 °C to reduce the impacts of climate change [19].
In recent decades, Community Forest Management (CFM) has emerged as a significant framework for forest management globally [20]. It involves community-based and co-management systems and encompasses many types of entities, including community forests, community protected areas, community fisheries, and indigenous community land titling. CFM plays a crucial role in sustainable forest management and local livelihood improvement. It has been found to contribute to a reduction in the over-exploitation of forest resources, the restoration of degraded land areas, and improved collaboration with local government agencies [21,22]. It can also provide multiple livelihood opportunities for community members, contributing to building both financial and technical capacity to deal with stresses, such as the negative impacts of climate change [23,24].
There are strong links between CFM and the REDD+ program. REDD+ provides financial, technical, and social benefits to communities by protecting forests, conserving wildlife, and establishing alternative livelihoods [25,26,27]. Conversely, CFM plays a key role in the effectiveness and sustainability of REDD+ [28]. Communities help REDD+ projects succeed by contributing their expertise in managing forests [29,30,31], including monitoring forests, protecting biodiversity, and increasing forest carbon stocks [22,32,33,34,35,36,37,38].
CFM is crucial for the success of REDD+ projects [39,40,41]. As such, the rights to access forest resources and the carbon rights of communities who are part of the CFM are critical [39,42]. Communities work more effectively when they have fully granted forest tenure and carbon rights. Carbon rights comprise two fundamental concepts: (1) property rights to sequester and store carbon contained in land, trees, etc., and (2) the rights to benefits that arise from the transfer of these property rights through emissions trading schemes [43,44]. Carbon rights underpin benefit-sharing mechanisms for stakeholders, especially communities, leading to lower deforestation and forest degradation rates, increasing forests’ carbon storage, improving forest governance [45], and contributing to the success of REDD+ projects [46]. REDD+ benefit-sharing mechanisms encompass a comprehensive range of institutional methods, institutions, and tools used to distribute funds and other advantages derived from REDD+ projects [47]. However, numerous studies indicate that many communities currently possess limited forest tenure and carbon rights [9,48,49,50,51,52,53,54].
Only when communities’ rights are fully recognized and legalized can they participate fully in decision-making processes related to REDD+ project design, implementation, management, and benefit-sharing [48,55,56]. Effective benefit-sharing mechanisms have the potential to support community livelihood development programs [57,58,59], contribute to communities’ capacities to withstand unexpected shocks, and enhance their resilience to climate change [60,61].
This review has three main objectives. The first objective is to explore how indigenous and local communities’ rights are being recognized in REDD+ projects in Cambodia. In particular, the concepts of free, prior, and informed consent (FPIC), safeguards principles, and grievance redress mechanisms will be introduced, and the effectiveness of how they are currently being implemented in REDD+ projects in Cambodia will be considered. The second objective is to investigate different benefit-sharing approaches employed in REDD+ projects in Cambodia. The final objective is to evaluate how REDD+ projects contribute to communities’ climate change resilience through livelihood development programs.
This paper is divided into seven main sections. Section 2 provides important background information on the drivers of deforestation and forest degradation in Cambodia. It also introduces community forests and outlines the scope of the REDD+ program in Cambodia. Section 3 then explores how FPIC, safeguards principles, and grievance redress mechanisms have been implemented by REDD+ projects in Cambodia. Next, Section 4 considers how REDD+ projects implement benefit-sharing arrangements and benefit distribution to different stakeholders, especially indigenous peoples and local communities. Section 5 then reviews the literature on how REDD+ projects utilize REDD+ benefits to help communities adapt to climate change impacts. Finally, Section 6 and Section 7 discuss the key findings in a wider context and identify potential areas for future research and policy recommendations for both Cambodia and beyond.

2. Background

2.1. Drivers of Deforestation and Forest Degradation in Cambodia

Cambodia has undergone considerable forest loss over the last 50 years. In 1973, Cambodia had 13.22 million hectares of forest, equivalent to 73.04% of land cover. By 2018, this was reduced to 8.5 million hectares, only 46.86% of land cover [62,63]. From 2001 to 2022, Cambodia experienced a decrease in humid primary forest area by 1.39 million hectares, which represents 52% of the total fall in tree cover during that time [27,64].
The Forest Carbon Partnership Facility identifies six direct drivers of deforestation and forest degradation in Cambodia: unsustainable logging; unsustainable wood fuel collection; agricultural expansion; the expansion of settlements; infrastructure development; and fire [65]. There are also many indirect drivers of deforestation and forest degradation in Cambodia. These include limitations associated with forestry governance including limited institutional capacity; weak policy implementation; inadequate law enforcement; a lack of transparency and accountability; low levels of stakeholder participation; a lack of incentives for sustainable forest management; and a lack of finance to support sustainable forest management. Deforestation and forest degradation is also being driven by broader social and economic trends in Cambodia including: population growth; high levels of poverty; new settlements and migration into forest areas; growing demand for forest resources; the increasing accessibility of forests; low agricultural yields; social norms associated with claiming land through utilization; and a limited awareness of the social and environmental benefits of forests [65,66,67,68].

2.2. Communities and Their Involvement in Forest Management in Cambodia

There are four main types of community forest management that have been involved in REDD+ projects in Cambodia: community forests (CFs), community protected areas (CPAs), indigenous community land titling (ICLTs), and community fisheries (CFis) (see Table 1).

2.3. Status of REDD+ Program in Cambodia

Cambodia’s first REDD+ project was established in 2008 in Oddar Meanchey province, with support from partners including Terra Global Capital, Pact, Children’s Development Association, and Community Forestry International [75]. At that time, there was no national REDD+ management body or official assistance from international organizations. Cambodia submitted a proposal for readiness planning to the Forest Carbon Partnership Facility (FCPF) and became a partner country of the UN-REDD Program in 2009. Cambodia signed a national program agreement with the UN-REDD Program in 2011 enabling Cambodia to receive both financial and technical assistance from the UN-REDD+ Program, leading to REDD+ preparation at the national level and REDD+ pilot project implementation at the sub-national and project levels [76].
To effectively coordinate and manage this national program, a taskforce and secretariat were established [77]. The role of the taskforce is to organize and oversee the development of strategies and terms of reference for REDD+ project implementation, make decisions on the implementation of REDD+ projects, monitor projects’ results, and report to the government. The role of the taskforce’s secretariat is to facilitate the formulation of policies and strategies for REDD+ in Cambodia by aiding the REDD+ taskforce. The secretariat is also responsible for implementing the vision of the taskforce to build a national REDD+ program, including organizing and coordinating technical and financial operations, as well as seeking cooperation from government agencies, development partners, NGOs, and other stakeholders. It also serves as the main focal point and coordinating mechanism for REDD+ implementation in Cambodia [78,79].
As of 2024, there are 11 REDD+ projects in Cambodia (as illustrated in Figure 1). Seven have been officially registered with Verra, a non-profit organization that manages the world’s leading voluntary carbon markets program, the Verified Carbon Standard (VCS) [80]. The Prey Lang REDD+ project is registered with a Joint Crediting Mechanism (JCM) developed by Japan to accurately assess Japan’s contributions to reducing or removing greenhouse gas emissions [81,82]. Additional REDD+ projects are currently being planned and developed [83].

2.4. The Legal Framework for REDD+ in Cambodia

The key national policy guiding REDD+ program implementation in Cambodia is the National REDD+ Strategy (2017–2026), which aims to reduce deforestation and forest degradation rates, conserve and sustainably manage forest and biodiversity resources, and contribute to poverty reduction. To achieve this goal, one of the guiding principles is to ensure full and effective participation of relevant stakeholders, including local communities and indigenous peoples [83]. Four REDD+ technical working groups have been established to support the REDD+ Secretariat in implementing the REDD+ strategy. The working groups oversee the direction and execution of REDD+ technical efforts, examining the best ways to implement REDD+ safeguards principles and benefit-sharing arrangements in REDD+ projects, and formulating technical recommendations in their respective areas of expertise. These teams consist of technical personnel from several government agencies and representatives from civil society, including indigenous peoples and non-governmental organizations.
In 2019, Cambodia submitted its First Summary of Information on Safeguards to the UNFCCC to show how it safeguards the rights of indigenous peoples and local communities when implementing REDD+ projects [84]. Table 2 summarizes the core elements of these social safeguard principles.

3. REDD+ Projects and Community Participation

3.1. Communities’ Roles in Implementing REDD+

Communities have many roles in REDD+ projects in Cambodia, including project monitoring, forest patrolling, reducing drivers of deforestation and forest degradation, and conserving forests and wildlife. For example, a study conducted by Nhem et al. [15] investigating community forests in Oddar Meanchey province and Kampong Thom province found that community members play crucial roles in forest patrolling, conserving and preserving forests and biodiversity, and participating in community forest decision-making processes.
Through voluntary international standards like the Verified Carbon Standard (VCS) and the Climate, Community, and Biodiversity Alliance (CCBA) Standard, REDD+ projects are increasingly integrating biodiversity conservation components into their project designs [85]. Communities play a crucial role gathering relevant biodiversity data and information in a rapid and cost-effective manner [86]. This role can build a sense of trust among community members in terms of being involved in REDD+ project implementation, aligning with the UNFCCC’s recognition of the full and effective engagement of local and indigenous peoples. Communities have also been participating in carbon monitoring as part REDD+ projects using low-cost and simple tools. For example, bamboo sticks and plastic rulers or calipers are used to measure tree diameters and calculate carbon storage [87,88]. Some communities are also involved in forest and carbon monitoring and reporting by using remote-sensing data produced by forestry experts, making a vital contribution to data collection and the effectiveness of REDD+ project implementation [89,90].
Communities also contribute to reductions in deforestation and forest degradation rates. For example, Pauly et al. [27] used satellite data, project information, and government economic land concession data to compare three Cambodian REDD+ projects (the Tumring REDD+ project, Cardamom REDD+ project, and Keo Seima REDD+ project). They found that these REDD+ projects significantly reduced deforestation by providing funding to targeted community forests, maintaining strict monitoring, and enforcing stringent laws throughout the project areas. This reduction in deforestation and forest degradation rates is critical, as it not only protects forest resources and biodiversity but also significantly contributes to climate change mitigation through emission reduction and carbon sinks [91].
Currently, there are 11 REDD+ projects with different sizes, estimated annual emission reduction rates, and crediting periods (see Table 3). For instance, with a project size of more than 465,000 ha, the Southern Cardamom REDD+ project has potential to reduce annual emissions by almost 4 million tons of CO2 equivalent [92].
FPIC processes establish conditions for people to exercise their fundamental right to negotiate the terms of externally imposed policies, programs, and activities that directly affect their livelihoods or wellbeing, and to give or withhold their consent to them [97,98]. REDD+ project proponents and carbon development partners apply FPIC principles to abide by VCS and JCM standards. Activities such as gathering villagers’ thumbprints and signing ceremonies were conducted in target villages and communities to show agreements required by the carbon standards [99].
There is limited literature documenting how FPIC processes were conducted in REDD+ projects. Milne and Mahanty [100] describe the FPIC process used in the Keo Seima REDD+ project. First, awareness-raising events about REDD+ and REDD+ social impact assessment were conducted across the project area. Next, the FPIC agreement was drafted, with input from government officers, the Wildlife Conservation Society (WCfS), and a contracted legal firm. The WCS was then instructed by the government to seek individual consent from at least 1000 households in the project area. Finally, once those consents had been obtained, a FPIC agreement signing ceremony was held. Community leaders were chosen as representatives to sign FPIC agreements with the Forestry Administration, agreeing on REDD+ implementation. Overall, Milne and Mahanty argued that the FPIC process in the Keo Seima project was inclusive.

3.2. Challenges Associated with Community Participation

3.2.1. Ineffective Implementation of Safeguards and Grievance Redress Mechanisms

Several studies provide evidence that REDD+ projects in Cambodia are not effectively implementing safeguard principles and grievance mechanisms [101,102,103,104,105,106]. Safeguard principles are one of the four key building blocks required by the UNFCCC’s COP19 that developing countries must have in place to receive results-based payments [107,108]. Grievance Redress Mechanisms (GRMs) are formal or informal processes for the resolution of complaints or disputes, involving organizations and individuals whose rights may be impacted by the implementation of REDD+ activities. They can range from communication to negotiation, mediation, or arbitration [109].
REDD+ projects receive carbon credits referred to as Verified Carbon Units (VCUs) [110]. Each VCU signifies a decrease or elimination of one ton of carbon dioxide equivalent (CO2e) achieved by a project. VCUs are defined by several quality assurance standards that are validated by the project validation and verification process, as well as Verra’s evaluation and approval. VCUs are ultimately acquired and decommissioned by an end user to mitigate their emissions. However, some argue VCUs are not designed for people in the tropics but for greenhouse gas emitters in the Global North [101,102,105]. For instance, it was never the intention of the Oddar Meanchey REDD+ project to offer direct monetary compensation to participants who would have to give up their access to forest areas. There was never a system to deliver direct payments to people or households that could serve as an incentive to conserve local forests. The project also never attempted to provide an analysis of opportunity costs or conduct forecasts of carbon prices to predict the required amount of cash needed to act as an incentive to maintain forests. Instead, VCUs were generated to sell to corporations such as Microsoft and Virgin, which increase values to their commodities and services [101]. The primary focus of the project was to utilize communities and forest resources to produce VCUs to sell with little regard for the potential costs to community members who may lose access to forest resources as a result of the project. As such, this project did not appropriately implement the REDD+ safeguards principles.
Exploitation of local communities, power imbalances, and inequities in decision-making processes can result in poor engagement and detrimental outcomes for local communities. Power imbalances cause social exclusion, preventing community forest members from receiving the benefits of REDD+ forest conservation activities. As a consequence, the distribution of benefits may unfairly favor those with greater wealth and involvement in decision-making processes [103,104]. For example, Persson and Prowse [111] researched two community forests in Kratie province to investigate how difficult it is for local forest users to set up formal institutional structures, coordinate collective action projects, and strengthen traditional and commercial property rights over a forest area. They found that younger and less affluent households were marginalized from official gatherings, observing limited benefits for participants, informal channels of information transmission that excluded women and poorer households, minimal levels of formalization, substantial enforcement costs, and significant external pressures from forestry authorities and local and international conservation organizations.
Work [102] also found that a REDD+ project in Kampong Thom province inadequately pays community forest members for conserving forest resources, offering them minimal compensation for protecting forests, which consumes their time, requires intensive labor, and places them in great danger from forestland encroachers, illegal loggers, and other forest offenders.

3.2.2. Weaknesses in the Application of CFM FPIC

There have been few studies about FPIC in REDD+ projects in Cambodia. Milne and Mahanty [100] studied REDD+ processes in Cambodia using the Keo Seima REDD+ project as a case study. They found that there were significant challenges in reaching a consensus due to significant inter- and intra-community heterogeneity. There were also issues of representation and creating meaningful agreements, as village chiefs were chosen to represent villagers and there was limited literacy among indigenous populations. They also found that, despite the formal processes, the FPIC implementation faced criticism for not fully addressing local demands or perspectives. Issues such as consent and customary rights were complicated by the project’s legal framework.
Others have observed similar deficiencies in consultation and engagement in other regions of Cambodia, finding that some community forest management committee decisions regarding REDD+ agreements with REDD+ project proponents may not be voluntary for all community members [105,112]. For example, Human Rights Watch [113] conducted a two-year investigation into the Cardamom REDD+ project’s impacts on indigenous peoples’ rights. Their investigation revealed that the REDD+ project operated for 31 months without seeking input from the Indigenous Chong people residing in the region, infringing on their right to free, prior, and informed consent for the project. Within the 31-month period, project operations encompassed significant determinations regarding the administration of almost 500,000 hectares of land, including the integration of eight Indigenous Chong communities into a national park.

3.3. Addressing the Challenges Associated with Community Participation

Successful implementation of REDD+ projects in Cambodia requires strong collaboration among stakeholders, particularly with active community participation [87,114]. Ensuring communities have adequate resources, capacity, and government support is vital for reducing deforestation and enhancing project outcomes. Collaboration between local communities, government agencies, NGOs, and international donors is crucial for overcoming challenges such as deforestation drivers and implementing sustainable forestry practices [15,115,116].
Effective community involvement in REDD+ is linked to reforms in monitoring and enforcement mechanisms. Locally adapted sanctions and fair compensation systems, coupled with access to community development funds, enable more effective governance of community forests [111,114,117]. Engaging marginalized communities, especially women and poor households, in decision-making is essential for the long-term success of these projects [113]. Strengthening the role of communities ensures that local knowledge and traditional forest management practices are incorporated into REDD+ project activities [3,86,87,89,118,119].
Furthermore, large-scale reforestation projects, such as those in Kratie province, highlight the need to shift the focus away from monoculture plantations to more inclusive, community-driven approaches that respect local land use and cultural practices [120]. Revising policies to prioritize social safeguards and ensure the FPIC of local communities has the potential to improve both environmental outcomes and social equity.
Informed by these studies, the efficacy of REDD+ in Cambodia is contingent upon robust community engagement, acknowledging their vital contribution to forest stewardship, conservation, and sustainable management. Securing substantive FPIC is crucial for empowering communities in decision-making, preventing marginalization, and ensuring authentic engagement. The effective implementation of safeguard principles and grievance redress mechanisms will secure community rights and bolster trust in REDD+ efforts. Enhancing the legal framework, especially with tenure security and carbon rights, is essential for empowering communities to manage and derive benefits from forest resources. Moreover, multi-stakeholder collaboration drawing upon both local knowledge and scientific and policy expertise can establish more inclusive, transparent, and effective governance frameworks, ensuring that REDD+ provides both environmental and social benefits.

4. Forest Tenure, Carbon Rights and Benefit-Sharing Mechanisms

4.1. Forest Tenure and Carbon Rights

If communities’ tenure and carbon rights are weak, their positions within REDD+ projects are also weak [98]. Forest tenure stipulates who owns forestland and who manages, uses, and makes decisions about forest resources [121,122]. The Forestry Law 2002 offers a provision that allows communities to access some forest resources for customary uses, including wild vegetables, mushrooms, rattan, resin, and timber for house building [11,120,123,124]. This means that villagers and community forest members can use forest resources solely for subsistence, not commercial purposes. For example, local people in the Cardamom Mountains do not have land titles for their land, which are state property, managed by the Forestry Administration [125]. However, this law partially recognizes indigenous peoples’ rights and allows these people to access land and forest resources for traditional use, which also allows communities and indigenous peoples to negotiate contracts to avoid deforestation using informal or customary rights [126].
There is a strong link between forest tenure, carbon rights, and benefit sharing [98,119,124,125,126,127]. Carbon rights comprise two fundamental concepts: (1) property rights to sequester and store carbon contained in land, trees, etc., and (2) the rights to benefits that arise from the transfer of these property rights through emissions trading schemes [128]. While existing policies, laws, and regulations in Cambodia acknowledge the customary use of local communities, the government currently owns carbon rights [115].
Most REDD+ projects provide support to CFM for forest tenure security activities. In implementing REDD+ projects, the risk of the exclusion of communities from lands and forests is real [124,126]. However, REDD+ is also an opportunity to legalize, strengthen, and secure long-term tenure over forest resources and land through forest carbon agreements with communities, which may, in turn, contribute to the success of REDD+ projects [125,126,127]. For instance, improving forest and land tenure is a core outcome of the Seima REDD+ project in the northeastern part of Cambodia, and it may serve as a more trusted community forest benefit compared to a direct financial payment [119,124]. Similarly, community forest land registration is one of the core objectives of the Tumring REDD+ project. As of September 2024, Tumring had successfully registered five community forests, with four at the final stage of the registration process, and plans to register a further seven in the future [129].
Different REDD+ projects have been trying different benefit-sharing models. For instance, Yeang [115] investigated the tenure arrangements of the Oddar Meanchey REDD+ project using in-depth and semi-structured interviews and field observation and found that communities still have access to forest resources even though carbon rights belong to the government. At that point, the government did not have any benefit-sharing arrangements in place. However, it agreed to allocate at least 50% of revenues from carbon credit sales to participating communities, based on Government Decision No. 699 in the Oddar Meanchey REDD+ project.
In contrast, the Keo Seima REDD+ project developed six principal stages of revenue distribution [130]. Transaction costs such as verification, issuance, registry, bank fees, and legal fees consume a small proportion of the gross sales. The remaining funds are considered net revenue. The Ministry of Environment, the government institution responsible for the Keo Seima Wildlife Sanctuary, takes 20% of the net revenue for different national conservation activities. The remaining 80% is used for direct project support, including cash for communities, project-strengthening activities, and operating reserves. The Tumring REDD+ project adopts and employs a similar REDD+ benefit-sharing model, allocating 10% of the budget for transaction costs, another 10% for a reservation fund, and 80% for direct community support [129]. Figure 2 summarizes how the revenue from carbon credit sales is distributed by REDD+ projects in Cambodia.

4.2. Challenges Associated with Forest Tenure, Carbon Rights and Benefit Sharing

4.2.1. Forest Tenure Issues and Lack of Recognition of Carbon Rights

Even though there are mechanisms in place, such as the UNFCCC’s safeguards and FPIC, resource access issues remain a challenge for CFM. Researching nine case studies from four countries in the Asia–Pacific, including Cambodia, Seth et al. [98] found that in some cases, REDD+ projects impair communities’ abilities to meet their needs by restricting access to forest resources. Likewise, Bourdier [105] discovered that REDD+ restricts community members from accessing forest resources, which they were dependent on before REDD+ projects were initiated. For example, Bunong communities can access forest resources, but sometimes they are strictly evaluated by a conservation NGO, which attempts to keep them away from the forests. Additionally, the payment scheme for environmental services currently being implemented relies on inadequate land security and a limited legal foundation [131].
Unclear forest tenure can lead to elite capture. Elite capture refers to circumstances in which elites influence development processes to align with their own interests and/or allocate development resources for personal benefit [132]. Some CF leaders, who are members of the CF management committee, may control local access to forest resources and take those resources for their own advantage [112]. Policies on forestry and wildlife are not fully and fairly implemented, leading to a lack of ownership and full access to forest resources for local communities [133].
The complicated, lengthy, and expensive land titling process is a fundamental issue for CFM. FAO and MRLG [134] pointed out that communal land titling procedures for indigenous communities must go through three to five ministries, taking from four to six years and costing around USD 50,000 per indigenous community registration. To register, indigenous communities must also not have any boundary conflicts with adjacent communities, which can be difficult to achieve, as there are often historical and contemporary disputes over territorial claims.

4.2.2. Unclear Benefit-Sharing Arrangements and Power Imbalances

Current policies do not provide comprehensive guidelines about benefit-sharing mechanisms [86,120]. There is no ‘one size fits all’ mechanism, and there have been unclear benefit-sharing arrangements for some REDD+ projects. For example, the Oddar Meanchey REDD+ project expected to make more than USD 50 million, with a unit price of USD 7 per ton of carbon dioxide equivalent, and half of this income was planned to be distributed to communities, prioritizing low-income households and applying an incentive-based approach [135]. However, there are no formal benefit-sharing mechanisms in place. When conducting field observations and 114 semi-structured interviews in five villages in this project area, Nathan and Pasgaard [136] found three main reasons for this. First, it is difficult to calculate people’s opportunity costs, as few community members hold legal land titles. There were immigrants moving into the project site, causing difficulties in assessing who should be compensated for a specific time. CF members protected forests, but these forests were also used by other villagers and members of the public, so the compensation calculations were extremely complicated. Second, the project is intended to keep the cost down, which may impact community compensation rates. Third, the project has a stronger position than communities. The project could avoid compensating marginalized community members, who have little power and no legal claims.
The power imbalance between REDD+ stakeholders is a key issue undermining effective benefit-sharing. Using qualitative interviews, field observation, and documents analysis, Pasgaard and Nielsen [104] investigated how a community forest in the Oddar Meanchey REDD+ project was established. They showed that the community forest has been dominated by powerful external actors (forestry authorities, local and international NGOs) rather than community members. These powerful external actors represent communities in defining community forest boundaries, problems in communities, and conceptualizing conservation services before even approaching communities. This abuse of power negatively affects benefit-sharing arrangements, as communities may not receive the benefits they deserve from the REDD+ project. Similarly, Pasgaard and Chea [103] also found that benefits from CF/REDD+ are not effectively distributed to vulnerable households due to physical impediments and a lack of resources or information that limit their access to forest resources. Furthermore, their capacity to reap the advantages of forest conservation is similarly constrained by social marginalization enabled by existing power dynamics. Conversely, the benefits are predominantly favored towards the more affluent households that participate in forest conservation activities and decision-making.

4.3. Addressing the Challenges Associated with Forest Tenure, Carbon Rights and Benefit Sharing

In Cambodia, community land titles play a vital role as legal tools to safeguard the rights of local communities, especially in situations involving disputes with influential entities such as investors, military forces, or forestland encroachers. These titles provide a solid basis for protecting claims to land and guaranteeing legal precision in conflicts over ownership [134]. Ensuring solid land titles is crucial for the efficient operation of REDD+. These titles not only establish ownership but also identify the parties eligible to receive financial compensation through REDD+ contracts, which may thereafter be legally enforced [131,136].
Furthermore, the matter of carbon rights is crucial in the administration and allocation of advantages derived from REDD+ projects [137]. The establishment of a legal framework for carbon rights is essential, as it directly affects the distribution of both carbon and non-carbon benefits among stakeholders. The legal framework in Cambodia may require modifications to precisely delineate carbon rights and their connection to land tenure [120].
A fair distribution of benefits is essential to promote participation and mitigate deforestation. Advocates of REDD+ projects and the government should guarantee the establishment of robust benefit-sharing systems to incentivize involvement from communities and other relevant parties [75,115,120,136]. The establishment of a robust benefit-sharing framework is essential for REDD+ to achieve its desired outcomes [138,139]. To enhance the livelihoods of forest-dependent communities, it is imperative that this model incorporates both monetary and non-monetary advantages [140]. The establishment of an equitable remuneration structure for individuals within a community, considering the opportunity costs, is crucial for achieving sustained success [135]. Furthermore, financial technology plays a crucial role in efficiently and securely transferring benefits, therefore fostering greater equity and traceability in the system [141]. To enhance the effectiveness of the REDD+ program in Cambodia, a collaborative strategy that incorporates findings from previous experiences to develop strong benefit-sharing protocols is needed [140].
Building on these findings, the effectiveness of REDD+ in Cambodia depends on resolving ongoing governance and equity issues. Defining carbon rights and ensuring community tenure are essential not only for legal compliance but also for facilitating substantial engagement and enduring sustainability. In the absence of definitive ownership, communities are susceptible to exclusion from financial advantages, hence diminishing incentives for forest protection. Transparent and inclusive benefit-sharing systems are essential to avert elite capture and guarantee that marginalized groups, particularly women and economically disadvantaged households, have their equitable share. Enhancing institutional capacity, along with focused financial assistance, can improve local participation and guarantee that REDD+ provides more equitable livelihood benefits and climate adaptation practices. A participatory and rights-based approach is essential to transform REDD+ into a genuinely sustainable and socially equitable forest governance paradigm.

5. Livelihood Improvement and Climate Change Adaptation

5.1. REDD+, Livelihood Development and Climate Change Adaptation

REDD+ generates carbon credits through conservation activities, resulting in emission reductions and, in turn, receiving compensation through carbon credit sales. The funds from the sales can be used to conserve forests, improve biodiversity, and improve the livelihoods of communities [142]. In Cambodia, incomes from forests have been playing a significant role in supporting poor rural households’ livelihoods and reducing income inequality and poverty [15,143]. Most REDD+ projects provide opportunities for local communities to improve their livelihoods and land tenure and contribute to sustainable development goals, but some do not [140,144]. REDD+ projects offer diverse project activities, such as training in agricultural techniques, undertaking soil rehabilitation, and establishing small enterprises for non-timber forest products. These activities generate income for community forest members, resulting in improving their livelihoods [129,138,145,146].
According to Pauly et al. [27] and Pauly and Tosteson [91], some REDD+ projects have offered resources for community development components, leading them to continue conserving forest resources. Likewise, Ken et al. [139] pointed out that REDD+ projects increase overall capital assets and improve the livelihoods of local communities. They applied the Sustainable Livelihood Framework developed by Scoones [147], using 14 indicators of livelihood capital assets in the Keo Seima REDD+ project from 2010 to 2018 and the Oddar Meanchey REDD+ project from 2008 to 2018. They found that there had been a notable rise in the total capital assets seen in the two locations. In particular, they found that physical capital assets (biodiversity, improvement in forest coverage, and environmental conservation) increased by 57.4–60.7%, while human capital (technical assistance, environmental education, skills and knowledge, and capacity building) increased by 26.5–34.9%.
There have been no specific studies regarding how REDD+ projects support climate change adaptation in Cambodia. However, there have been project activities implemented by government institutions, REDD+ projects, and development partners, which may help communities adapt to climate change. For example, communities have been trained in sustainable agricultural practices such as agroforestry, which integrates trees with crops and livestock. This not only diversifies income sources but also enhances soil fertility and resilience to climate impacts like droughts and floods [148,149]. By leveraging the natural beauty and biodiversity of forests, communities may also generate revenue through tourism activities. This provides financial incentives for forest conservation and increases community resilience by diversifying income streams [150]. Harvesting and selling non-timber forest products such as resin, honey, and medicinal plants can also provide additional income for communities. This approach allows communities to benefit economically from forests without resorting to deforestation. Training in sustainable harvesting techniques ensures that these resources remain available for future use, contributing to both economic and environmental resilience [129,151].
Access to microfinance and support for small business development help communities invest in diversified income-generating activities. For example, microfinance institutions and banks provide loans and grants to communities to start small enterprises like crafts and local trading [152]. Since 2018, O Taneung community forest members in Kratie province have been overseeing a community forest saving group that they initiated with USD 1000 in financial support from the Regional Community Forestry Training Center and the Swiss Agency for Development and Cooperation [153]. By 2020, the fund had expanded to about USD 3000, catering to approximately 35 families. Households have utilized their loans to purchase seeds, fertilizers, and other agricultural commodities. Programs raising awareness about the benefits of forest conservation and sustainable livelihoods also help communities adapt to climate change by adopting practices that enhance resilience and reduce vulnerability [145].

5.2. Challenges Associated with Livelihood Improvement and Climate Change Adaptation

It is important to note that some REDD+ projects have negatively impacted the livelihoods of local communities. After a forest restoration project by the Korean company, Think Biotech, had been in operation for some time, local villagers found themselves with not enough jobs to secure their daily livelihoods, as the project’s worker demand dropped and people could not go into the forests for non-timber and timber products as they did before [120]. Similarly, a study by Ken et al. [139] indicated that the natural capital asset experienced a significant decrease of approximately 31% and 26% in the Oddar Meanchey REDD+ and Keo Seima REDD+ locations, respectively. They argued that reason for the decline was that the absence of consistent financial backing focused on carbon emissions led to a loss of confidence between the local community and the project developer. As a result, the practice of illegal logging and clearing of land for personal profit continued, further contributing to the depletion of natural resources.
Implementing effective climate change adaptation measures requires significant financial resources. Despite international support, the funds available often fall short of the needs for comprehensive adaptation strategies. Securing sustained and adequate financing for long-term projects is a persistent challenge [154,155]. Weak institutional capacity and governance structures can hinder the effective implementation of REDD+ programs. Issues such as unclear land tenure, limited enforcement of forestry laws, and bureaucratic inefficiencies continue to impede progress [155,156]. Ensuring the meaningful participation of local communities, particularly indigenous peoples, in REDD+ projects is crucial but challenging. There can be gaps in knowledge, capacity, and trust between project implementers and local communities [157].

5.3. Addressing the Challenges Associated with Livelihood Improvement and Climate Change Adaptation

REDD+ projects in Cambodia offer significant opportunities for enhancing community livelihoods and climate change adaptation. Communities can benefit from sustainable forest practices, biodiversity monitoring, and alternative income streams like ecotourism and the sale of non-timber forest products [89,133]. These activities help mitigate the financial uncertainties of carbon markets by diversifying income sources [139]. By investing in sustainable agriculture, renewable energy, and social enterprises, REDD+ projects can provide long-term, self-sustaining revenue for local communities while encouraging forest conservation.
Reducing deforestation and carbon emissions can also be achieved through practical household-level changes. For example, introducing improved cooking stoves and mosquito nets reduces the need for fuelwood and prevents deforestation [158]. These small interventions not only lower carbon emissions but also contribute to better livelihoods for communities reliant on forest resources. Such projects require financial support to encourage widespread adoption and to maximize environmental and economic benefits.
Sustainable financing sources can help communities better cope with climate change by supporting their involvement in REDD+ projects. Through CFM, communities can benefit from forest resources and carbon credit sales, improving livelihoods and resilience [153,159]. Empowering communities to manage natural resources enhances environmental sustainability [154,160]. Climate adaptation techniques, such as drought-resistant crops and efficient irrigation, promoted by the Ministry of Agriculture, Forestry, and Fisheries, help farmers adapt to changing conditions [161]. The integration of local knowledge with scientific data can improve adaptation strategies and resilience [162]. REDD+ projects can also actively promote climate adaptation strategies and disaster preparedness to enhance both environmental sustainability and the long-term resilience of local populations [163].
REDD+ offers a significant chance to improve community livelihoods and climate resilience. However, its efficacy hinges on equitable execution. Establishing equitable benefit-sharing arrangements is essential to avert inequalities in access to financial incentives and alternative revenue streams. Enhancing support for diversified and sustainable livelihoods, including agroforestry and ecotourism, can bolster economic stability while diminishing reliance on forest exploitation. However, focused capacity-building activities are essential to provide communities with the technical expertise and resources necessary for implementing climate adaptation practices. Robust collaboration among local communities, governmental bodies, and NGOs will be crucial for integrating traditional knowledge with contemporary adaptation measures, promoting enduring resilience, and guaranteeing that REDD+ effectively provides both environmental and economic benefits.

6. Discussion

The literature demonstrates a variety of opportunities and challenges associated with incorporating Community Forest Management (CFM) into REDD+ projects. CFM has strengthened REDD+ effectiveness by leveraging local knowledge, fostering community ownership, and encouraging sustainable forest management practices [15,50,86,105,111,117,164,165]. CFM has also contributed to enhancing livelihoods and climate resilience. However, ongoing issues relating to governance, benefit-sharing, and land tenure continue to pose significant challenges [40,166].

6.1. REDD+ Governance and Community Participation

Governance structures play a critical role in REDD+ outcomes. However, persistent weaknesses such as unclear policies, limited enforcement, and inconsistent FPIC application hinder effective implementation [25,41,51,167,168,169]. While some argue that decentralized governance improves community-led forest management [170], others suggest that hybrid models, balancing national oversight with local engagement, yield better results [50,171]. Sawathvong et al. [169] warned that central agencies in Laos dominate REDD+ governance, limiting non-state stakeholder participation in REDD+ consultation processes of the REDD+ program. Lozano et al. [172] reported that indigenous organizations in Peru have gained influence in REDD+ governance, but true inclusiveness is still needed. Tiki et al. [173] found that despite supportive legal frameworks in Ethiopia, enforcement and implementation remain weak, requiring stronger local policy execution. Aryal et al. [174] emphasized integrating place-based values, decentralization, and flexible REDD+ program designs while ensuring fair carbon pricing and regulatory oversight of voluntary carbon markets. Nantongo et al. [175] highlighted the need for context-specific governance and economic safety nets in Tanzania. Gauthier [176] underscored the to center indigenous decision-making rather than institutional hegemony in REDD+ governance.
Chorito and Assefa [177] highlighted Ethiopia’s strong institutional alliances but stressed that addressing power imbalances through collaborative governance and community involvement is key to equitable forest management. Osborne et al. [178] further advocated for a climate justice approach that prioritizes indigenous rights, tackling both technical carbon accounting concerns and broader socio-economic inequalities. Osei [179] emphasized that political will and strategic funding opportunities are essential for fostering REDD+ collaboration in Ghana. Sunderlin et al. [180] found that while conditional incentives remain key to REDD+, communities benefiting from multiple interventions, including non-conditional benefits, were more likely to adopt sustainable land-use changes in six countries, including Brazil, Cameroon, Indonesia, Peru, and Vietnam. Vijitharan et al. [181] highlighted the need for continuous REDD+ policy evaluations in Sri Lanka, recommending cross-referencing national and UNFCCC data to adapt to changing dynamics. These authors call for enhanced policy enforcement, inclusive governance, and stronger social safeguards to ensure that REDD+ effectively balances environmental integrity with equity and long-term community benefits.

6.2. Forest Tenure, Carbon Rights and Benefit-Sharing Mechanisms

Tenure security and carbon rights are critical to REDD+ success. Mahanty et al. [126], Yeang [115], Baird [11], Agyei [165], and Bastakoti and Davidsen [50] stressed the importance of legal tenure recognition for promoting community participation, while Evans et al. [119], Chapman et al. [118], and Awung and Marchant [40] showed that secure tenure and clear carbon rights increase community engagement. However, Krister et al. [166] highlighted persistent wealth inequalities in benefit-sharing, which often marginalize vulnerable groups. Lord [182] further critiqued REDD+ governance, showing how tenure conflicts, overlapping authorities, and top-down decision-making weaken local governance and exacerbate land insecurity. Duchelle et al. [183] and Joanes et al. [184] argued that policy reforms are necessary to ensure equitable benefit distribution and prevent elite capture. There is a consensus within the literature regarding the necessity for clear tenure, political responsibility, and locally derived governance solutions.
Shah and Race [185] advocated for integrated policy approaches addressing tenure, equity, and financial incentives to enhance REDD+ projects. Aryal et al. [186] highlighted transparency gaps in benefit-sharing and indigenous participation, recommending digital monitoring, carbon price adjustments, and stronger safeguards. Dugasseh et al. [187] called for community-level sensitization, inclusive decision-making, and tenure registration to ensure fair benefit distribution in REDD+ projects in Ghana. Based on their analysis of REDD+ projects in Indonesia, Wahyudi et al. [188] suggested that direct distribution of REDD+ funds is the most equitable approach while advocating for flexible, localized fund management mechanisms. These studies highlight the interconnected challenges of tenure security, carbon rights, and benefit-sharing, emphasizing the need for policy reforms, inclusive governance, and financial transparency to ensure REDD+ delivers fair and sustainable environmental and livelihood benefits.

6.3. Livelihood Improvement and Climate Change Adaptation

REDD+ projects have had mixed effects on livelihoods. Nantongo et al. [175] found that REDD+ had neutral effects on total income in Tanzania. Flanery et al. [31] found that REDD+ has the potential to support livelihoods if it aligns with the needs of communities. Ensuring that these communities can actively participate in its development and implementation in Cameroon may help them safeguard their livelihoods while benefiting from the program. Joanes et al. [184], Ken et al. [139], and Dieng et al. [171] highlighted that alternative income sources like agroforestry and ecotourism have boosted local economies in Kenya, Cambodia, and Senegal, while Kumar et al. [189] and McElwee et al. [167] cautioned that land-use restrictions have negatively impacted some communities Vietnam and India. Atela et al. [190] suggested that directing REDD+ funds to vulnerable regions can enhance both mitigation and adaptation efforts in Kenya. Additionally, REDD+ projects also help community members to adapt to climate change impacts. McElwee et al. [167] found that strengthening household adaptive capacity through REDD+ activities is essential. They argued that future REDD+ action plans in Vietnam should better integrate adaptation strategies, ensuring that both livelihoods and forest conservation are considered together. Learning from past experiences can help prevent increased climate vulnerability among participating communities. Paris [191] suggested that REDD+ benefits have indirectly enhanced adaptation in Indonesia, but to maximize these gains, project design should explicitly include adaptation objectives, implement safeguard measures, and ensure local support for adaptation efforts. These studies highlight that effective implementation, community participation, and strategic fund allocation can help maximize both livelihood and adaptation benefits. Integrating adaptation objectives and safeguard measures into REDD+ design will be crucial to enhancing resilience and ensuring sustainable outcomes for participating communities.

7. Conclusions

The integration of Community Forest Management (CFM) into REDD+ frameworks has the potential to support both conservation and socio-economic goals. However, a range of factors continue to constrain the effectiveness of REDD+ projects. While CFM has proven successful in enhancing local engagement, preserving biodiversity, and strengthening climate resilience through indigenous knowledge and sustainable land management, REDD+ frameworks sometimes introduce obstacles rather than solutions. Weak enforcement mechanisms, tenure insecurity, unclear carbon rights, and the inconsistent application of free, prior, and informed consent (FPIC), safeguard principles, and grievance redress mechanisms continue to hinder equitable outcomes. Strengthening FPIC processes and inclusive governance practices is essential to enhancing accountability, legitimacy, and respect for indigenous and local communities’ rights in REDD+ implementation.
Securing land tenure and providing legal recognition are fundamental to ensuring sustained community involvement in REDD+. However, issues such as elite capture and unequal wealth distribution persist, undermining the fairness of benefit-sharing. To address these gaps, legal tenure must be accompanied by appropriate financial support and the establishment of transparent, inclusive benefit-sharing frameworks. Strengthening governance structures and policy clarity, combined with innovative financial tools, such as locally adapted carbon credit schemes, can enhance the equity and long-term viability of REDD+ projects. A focus on fair distribution is particularly important for ensuring that marginalized groups meaningfully benefit from conservation initiatives.
Despite REDD+’s potential to contribute to climate adaptation, most projects in Cambodia and beyond have yet to integrate explicit adaptation measures. As a result, vulnerable communities remain exposed to climate-related risks. Incorporating locally relevant adaptive strategies, such as diversified livelihoods, agroforestry, and community-based resource management, into REDD+ initiatives is vital. These approaches can improve resilience while supporting the program’s broader environmental objectives.
The literature highlights several crucial opportunities to improve CFM-REDD+ effectiveness, including the following.
  • Investing in strengthening local governance structures and institutional capacity to enable effective forest management and REDD+ implementation;
  • Strengthening FPIC and participatory processes to enhance participatory decision-making, accountability, and legitimacy;
  • Encouraging collaboration between governments, communities, NGOs, and the private sector to foster inclusive and coherent forest governance;
  • Coupling legal recognition of tenure with financial support to maintain community commitment;
  • Establishing transparent benefit-sharing mechanisms to prevent unfair benefit distribution and promote social inclusion;
  • Facilitating access to sustainable financing and carbon markets through blended finance models;
  • Distributing funds to the most vulnerable and incorporating adaptive strategies into REDD+ projects to support both livelihood diversification and climate resilience;
  • Promoting community-based monitoring systems to support transparent, low-cost, and locally driven monitoring, reporting, and verification processes, curbing illegal forestland clearing for sales and illegal logging;
  • Undertaking regular monitoring and evaluation of social and equity outcomes to ensure REDD+ interventions achieve real impacts that address community needs.
By addressing these key issues, policymakers and stakeholders can work towards achieving a more inclusive, efficient, and resilient CFM-REDD+ model that reconciles conservation aims with local development requirements, thereby enhancing sustainable forest management in Cambodia and beyond. Cambodia’s experience offers significant insights for REDD+ projects in other parts of the world, highlighting the necessity of meaningful community engagement, secure land tenure, and governance mechanisms that reconcile conservation objectives with the needs of local communities.
Additional research is needed to investigate the application of REDD+ safeguard principles, including FPIC and grievance mechanisms, and the implementation of benefit-sharing mechanisms. Gaining a comprehensive understanding of how these mechanisms function in real-world scenarios would offer valuable insights into opportunities to enhance the governance and efficacy of REDD+ programs in Cambodia and internationally.

Author Contributions

C.Y. designed the research, collected and analyzed the literature, and planned and wrote the manuscript; K.F.H. and D.P. supervised the research and contributed to planning, revising, and editing the manuscript. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by a Manaaki New Zealand Scholarship from the New Zealand Ministry for Foreign Affairs and Trade.

Data Availability Statement

The data presented in this study are available on request from the corresponding author.

Conflicts of Interest

The authors declare no conflicts of interest.

References

  1. UN-REDD. UN-REDD Program Fact Sheet about REDD+. Available online: https://www.un-redd.org/sites/default/files/2021-10/Fact%20Sheet%201-%20About%20REDD3.pdf (accessed on 28 February 2025).
  2. UNFCCC. What is REDD+? Available online: https://unfccc.int/topics/land-use/workstreams/redd/what-is-redd (accessed on 28 February 2025).
  3. Fujisaki, T.; Hyakumura, K.; Scheyvens, H.; Cadman, T. Does REDD+ ensure sectoral coordination and stakeholder participation? A comparative analysis of REDD+ national governance structures in countries of Asia-Pacific region. Forests 2016, 7, 195. [Google Scholar] [CrossRef]
  4. Gupta, H. Understanding Stakeholders’ Perspective on REDD+ Implementation as a Multi-Sectoral Approach. In Climate Change, Food Security and Natural Resource Management; Behnassi, M., Pollmann, O., Gupta, H., Eds.; Springer: Cham, Switzerland, 2019. [Google Scholar] [CrossRef]
  5. Berry, N.; Harley, R.; Ryan, C. Enabling communities to benefit from REDD+: Pragmatic assessment of carbon benefits. Carbon Manag. 2013, 4, 571–573. [Google Scholar] [CrossRef]
  6. Boer, H. Welfare environmentality and REDD+ incentives in Indonesia. J. Environ. Policy Plan. 2017, 19, 795–809. [Google Scholar] [CrossRef]
  7. Hiratsuka, M.; Bounithiphonh, C.; Sichanthongthip, P.; Furuta, T.; Suzuki, K.; Kobayashi, N.; Chikaraishi, H.; Phongoudome, C.; Amano, M. Variations in village-level performances related to reducing deforestation and forest degradation associated with a REDD+ project in northern Lao People’s Democratic Republic. Environ. Dev. Sustain. 2021, 23, 2762–2784. [Google Scholar] [CrossRef]
  8. Appiah, D.O.; Bugri, J.; Forkuo, E.K.; Yamba, S. Agricultural and Forest Land Use Potential for REDD+ among Smallholder Land Users in Rural Ghana. Int. J. For. Res. 2016, 2016, 7218305. [Google Scholar] [CrossRef]
  9. Bernard, F.; Minang, P. Community forestry and REDD+ in Cameroon: What future? Ecol. Soc. 2019, 24. [Google Scholar] [CrossRef]
  10. Howell, S. ‘No RIGHTS–No REDD’: Some Implications of a Turn Towards Co-Benefits. Forum Dev. Stud. 2014, 41, 253–272. [Google Scholar] [CrossRef]
  11. Baird, I. ‘Indigenous Peoples’ and land: Comparing communal land titling and its implications in Cambodia and Laos. Asia Pac. Viewp. 2013, 54, 269–281. [Google Scholar] [CrossRef]
  12. Angelsen, A.; Martius, C.; de Sy, V.; Duchelle, A.E.; Larson, A.M.; Pham, T.T. Conclusions: Lessons for the path to a transformational REDD+. In Transforming REDD+: Lessons and New Directions; Angelsen, A., Martius, C., De Sy, V., Duchelle, A.E., Larson, A.M., Thuy, T.P., Eds.; CIFOR: Bogor, Indonesia, 2018; pp. 203–214. [Google Scholar]
  13. DiGiano, M.; Stickler, C.; David, O. How Can Jurisdictional Approaches to Sustainability Protect and Enhance the Rights and Livelihoods of Indigenous Peoples and Local Communities? Front. For. Glob. Change 2020, 30, 40. [Google Scholar] [CrossRef]
  14. Kumar, R.; Kumar, A.; Saikia, P. Deforestation and Forests Degradation Impacts on the Environment. In Environmental Degradation: Challenges and Strategies for Mitigation; Singh, V.P., Yadav, S., Yadav, K.K., Yadava, R.N., Eds.; Springer International Publishing: Cham, Switzerland, 2022; pp. 19–46. [Google Scholar] [CrossRef]
  15. Nhem, S.; Lee, Y.J.; Phin, S. Policy implications for community-managed forestry in Cambodia from experts’ assessments and case studies of community forestry practice. J. Mt. Sci. 2018, 15, 2531–2551. [Google Scholar] [CrossRef]
  16. IUCN. Deforestation and Forest Degradation. Available online: https://www.iucn.org/resources/issues-brief/deforestation-and-forest-degradation (accessed on 28 February 2025).
  17. UNFCCC. A Decade of REDD+: Notable Achievements by Forest Nations. Available online: https://unfccc.int/news/a-decade-of-redd-notable-achievements-by-forest-nations (accessed on 28 February 2025).
  18. UNFCCC. Lima REDD+ Information Hub. Available online: https://redd.unfccc.int/info-hub.html (accessed on 28 February 2025).
  19. Rastogi, A. When and where the climate threshold will be reached. Nat. Comput. Sci. 2023, 3, 121. [Google Scholar] [CrossRef] [PubMed]
  20. Arts, B.; de Koning, J. Community Forest Management: An Assessment and Explanation of its Performance Through QCA. World Dev. 2017, 96, 315–325. [Google Scholar] [CrossRef]
  21. Haji, L.; Valizadeh, N.; Hayati, D. The Role of Local Communities in Sustainable Land and Forest Management. In Spatial Modeling in Forest Resources Management: Rural Livelihood and Sustainable Development; Shit, P.K., Pourghasemi, H.R., Das, P., Bhunia, G.S., Eds.; Springer International Publishing: Cham, Switzerland, 2021; pp. 473–503. [Google Scholar] [CrossRef]
  22. Fischer, H.W.; Chhatre, A.; Duddu, A.; Pradhan, N.; Agrawal, A. Community forest governance and synergies among carbon, biodiversity and livelihoods. Nat. Clim. Change 2023, 13, 1340–1347. [Google Scholar] [CrossRef]
  23. Sedhain, J.; Franco, I.B.; Lamont, S. Sustainable Forest Management: Community Forestry’s Contribution to Build Climate-Resilient Communities in Nepal. In Corporate Approaches to Sustainable Development: International Experiences and Insights; Franco, I.B., Ed.; Springer Nature Singapore: Singapore, 2022; pp. 179–198. [Google Scholar] [CrossRef]
  24. Ekanayake, E.M.B.P.; Xie, Y.; Ahmad, S.; Geldard, R.P.; Nissanka, A.H.S. Community Forestry for livelihood Improvement: Evidence from the intermediate zone, Sri lanka. J. Sustain. For. 2022, 41, 1–17. [Google Scholar] [CrossRef]
  25. Lawlor, K.; Madeira, E.; Blockhus, J.; Ganz, D. Community Participation and Benefits in REDD+: A Review of Initial Outcomes and Lessons. Forests 2013, 4, 296–318. [Google Scholar] [CrossRef]
  26. Shrestha, S.; Karky, B.; Karki, S. Case Study Report: REDD+ Pilot Project in Community Forests in Three Watersheds of Nepal. Forests 2014, 5, 2425–2439. [Google Scholar] [CrossRef]
  27. Pauly, M.; Crosse, W.; Tosteson, J. High deforestation trajectories in Cambodia slowly transformed through economic land concession restrictions and strategic execution of REDD+ protected areas. Sci. Rep. 2022, 12, 17102. [Google Scholar] [CrossRef]
  28. Pelletier, J.; Gélinas, N.; Skutsch, M. The Place of Community Forest Management in the REDD+ Landscape. Forests 2016, 7, 170. [Google Scholar] [CrossRef]
  29. Angelsen, A.; Brockhaus, M.; Kanninen, M.; Sills, E.O.; Sunderlin, W.D.; Wertz-Kanounnikoff, S. Realising Redd+: National Strategy and Policy Options; CIFOR: Bogor, Indonesia, 2009. [Google Scholar] [CrossRef]
  30. Barletti, J.P.S.; Larson, A. Rights Abuse Allegations in the Context of REDD+ Readiness and Implementation: A Preliminary Review and Proposal for Moving Forward; CIFOR: Bogor, Indonesia, 2017. [Google Scholar] [CrossRef]
  31. Flanery, A.; Mbatu, R.; Johns, R.A.; Stewart, D. Rural Community Agency in Cameroon: Interactions with Forest Policies and the REDD+ Climate Change Regime. Forests 2022, 13, 617. [Google Scholar] [CrossRef]
  32. Danielsen, F.; Skutsch, M.; Burgess, N.; Jensen, P.M.; Andrianandrasana, H.T.; Karky, B.; Lewis, R.E.; Lovett, J.; Massao, J.; Ngaga, Y.; et al. At the heart of REDD+: A role for local people in monitoring forests? Conserv. Lett. 2011, 4, 158–167. [Google Scholar] [CrossRef]
  33. Torres, A.; Skutsch, M. Special Issue: The Potential Role for Community Monitoring in MRV and in Benefit Sharing in REDD+. Forests 2015, 6, 244–251. [Google Scholar] [CrossRef]
  34. Pasgaard, M.; Sun, Z.; Müller, D.; Mertz, O. Challenges and opportunities for REDD+: A reality check from perspectives of effectiveness, efficiency and equity. Environ. Sci. Policy 2016, 63, 161–169. [Google Scholar] [CrossRef]
  35. Lyver, P.O.B.; Timoti, P.; Jones, C.J.; Richardson, S.J.; Tahi, B.L.; Greenhalgh, S. An indigenous community-based monitoring system for assessing forest health in New Zealand. Biodivers. Conserv. 2017, 26, 3183–3212. [Google Scholar] [CrossRef]
  36. Murthy, M.S.R.; Gilani, H.; Karky, B.S.; Sharma, E.; Sandker, M.; Koju, U.A.; Khanal, S.; Poudel, M. Synergizing community-based forest monitoring with remote sensing: A path to an effective REDD+ MRV system. Carbon Balance Manag. 2017, 12, 19. [Google Scholar] [CrossRef]
  37. Eisenbarth, S.; Graham, L.; Rigterink, A.S. Can community monitoring save the commons? Evidence on forest use and displacement. Proc. Natl. Acad. Sci. USA 2021, 118, e2015172118. [Google Scholar] [CrossRef]
  38. Bender, S.; Tekle, M. Community Action for Biodiversity and Forest Conservation and Adaptation to Climate Change in the Wild Coffee Forests (CAFA). In Handbook of Climate Change and Biodiversity; Leal Filho, W., Barbir, J., Preziosi, R., Eds.; Springer International Publishing: Cham, Switzerland, 2019; pp. 79–92. [Google Scholar] [CrossRef]
  39. Corbera, E.; Estrada, M.; May, P.; Navarro, G.; Pacheco, P. Rights to Land, Forests and Carbon in REDD+: Insights from Mexico, Brazil and Costa Rica. Forests 2011, 2, 301–342. [Google Scholar] [CrossRef]
  40. Awung, N.S.; Marchant, R. Transparency in benefit sharing and the influence of community expectations on participation in REDD+ Projects: An example from Mount Cameroon National Park. Ecosyst. People 2020, 16, 78–94. [Google Scholar] [CrossRef]
  41. Birhan, E.; Assefa, E.; Petrova, M. Challenges of Forest Governance in Addressing Redd+: Status, Effects And Prospects. The Case of Bale Eco-Region, Oromia Regional State, Ethiopia. Geogr. Environ. Sustain. 2021, 14, 185–195. [Google Scholar] [CrossRef]
  42. Asare, R.; Kyei, A.; Mason, J. The community resource management area mechanism: A strategy to manage African forest resources for REDD+. Philos. Trans. R. Soc. B Biol. Sci. 2013, 368, 20120311. [Google Scholar] [CrossRef]
  43. UN-REDD. Carbon Rights and the Importance of Benefit Sharing. Available online: https://www.un-redd.org/post/carbon-rights-and-importance-benefit-sharing#:~:text=The%20term%20carbon%20rights%20comprises%20two%20fundamental%20concepts:%201)%20the (accessed on 28 February 2025).
  44. FAO. Voluntary Guidelines on the Responsible Governance of Tenure of Land, Fisheries and Forests in the Context of National Food Security; FAO: Rome, Italy, 2022. [Google Scholar] [CrossRef]
  45. Stevens, C.; Winterbottom, R.; Springer, J.; Reytar, K. Securing Rights, Combating Climate Change: How Strengthening Community Forest Rights Mitigates Climate Change; World Resources Institute: Washington, DC, USA, 2014. [Google Scholar]
  46. Peskett, L.; Brodnig, G. Carbon Rights in REDD+: Exploring the Implications for Poor and Vulnerable People; The World Bank: Washinton, DC, USA, 2010; p. 27. [Google Scholar]
  47. Wong, G.; Pham, T.T.; Valencia, I.; Luttrell, C.; Larson, A.M.; Yang, A.; Hasan, A.; Kovacevic, M.; Moeliono, M.; Dwisatrio, B.; et al. Designing REDD+ Benefit-Sharing Mechanisms: From Policy to Practice; CIFOR: Bogor, Indonesia, 2022. [Google Scholar]
  48. Chhatre, A.; Agrawal, A. Trade-offs and synergies between carbon storage and livelihood benefits from forest commons. Proc. Natl. Acad. Sci. 2009, 106, 17667–17670. [Google Scholar] [CrossRef]
  49. Chhatre, A.; Lakhanpal, S.; Larson, A.M.; Nelson, F.; Ojha, H.; Rao, J. Social safeguards and co-benefits in REDD+: A review of the adjacent possible. Curr. Opin. Environ. Sustain. 2012, 4, 654–660. [Google Scholar] [CrossRef]
  50. Bastakoti, R.R.; Davidsen, C. REDD+ and forest tenure security: Concerns in Nepal’s community forestry. Int. J. Sustain. Dev. World Ecol. 2014, 21, 168–180. [Google Scholar] [CrossRef]
  51. Dehm, J. Indigenous peoples and REDD+ safeguards: Rights as resistance or as disciplinary inclusion in the green economy? J. Hum. Rights Environ. 2016, 7, 170–217. [Google Scholar] [CrossRef]
  52. Corriveau-Bourque, A.; Almeida, F.; Fréchette, A. Uncertainty and Opportunity: The Status of Forest Carbon Rights and Governance Frameworks in Over Half of the World’s Tropical Forests; Rights and Resource Initiative: Washinton, DC, USA, 2018. [Google Scholar] [CrossRef]
  53. Enow, E.; Egute, T.O.; Albrecht, E. Forest tenure and rights: A constraint to community forest management in Cameroon and the REDD+ initiative. Int. J. Fores. Environ. 2021, 3, 121–129. [Google Scholar] [CrossRef]
  54. Cetera, K. Recognition of Forest Carbon Rights in Indonesia: A Constitutional Approach. Lentera Huk. 2022, 9, 151–176. [Google Scholar] [CrossRef]
  55. Royer, S.; Visser, L.E.; Galudra, G.; Pradhan, U.; van Noordwijk, M. Self-Identification of Indigenous People in Post-Independence Indonesia: A Historical Analysis in the Context of REDD+. Int. For. Rev. 2015, 17, 282–297. [Google Scholar] [CrossRef]
  56. Pham, T.; Moeliono, M.; Dwisatrio, B.; Yuwono, J.; Atmadja, S. REDD+ Benefit Sharing in Ethiopia: Policy and Stakeholder Perceptions Analysis. Int. For. Rev. 2022, 23, 476–491. [Google Scholar] [CrossRef]
  57. Cronkleton, P.; Bray, D.; Medina, G. Community Forest Management and the Emergence of Multi-Scale Governance Institutions: Lessons for REDD+ Development from Mexico, Brazil and Bolivia. Forests 2011, 2, 451–473. [Google Scholar] [CrossRef]
  58. Mustalahti, I.; Rakotonarivo, S. REDD+ benefit sharing mechanisms: Does it make a difference in equity? AgEcon Search 2012, 2012, 115–123. [Google Scholar] [CrossRef]
  59. Silas, S.R. REDD+ benefit sharing under models tested by pilot projects in Tanzania: Inputs towards developing national benefit-sharing mechanism models. Chin. J. Popul. Resour. Environ. 2016, 14, 38–44. [Google Scholar] [CrossRef]
  60. Awoniyi, S.O.M.; Amos, T.T. A Review of REDD+ Effectiveness at Ensuring Rural Community Resilience to Climate Change and Food Security in Nigeria. Niger. J. Agric. Econ. 2016, 6, 53–64. [Google Scholar] [CrossRef]
  61. Hajjar, R.; Engbring, G.; Kornhauser, K. The impacts of REDD+ on the social-ecological resilience of community forests. Environ. Res. Lett. 2021, 16, 024001. [Google Scholar] [CrossRef]
  62. Open Development Cambodia. Forests and Forestry. Available online: https://opendevelopmentcambodia.net/topics/forests-and-forestry/#:~:text=Cambodia%E2%80%99s%20forests%20have%20seen%20a%20significant%20reduction%20of,rubber%2C%20and%20an%20ongoing%20problem%20with%20illegal%20logging. (accessed on 28 February 2025).
  63. The National Council for Sustainable Development. Cambodia Forest Cover 2018. Available online: https://ncsd.moe.gov.kh/dcc/resource/Cambodia/Forest/Cover/2018 (accessed on 28 February 2025).
  64. Global Forest Watch. Cambodia. Available online: https://www.globalforestwatch.org/dashboards/country/KHM/ (accessed on 28 February 2025).
  65. Facility, F.C.P. Readiness Preparation Proposal (R-PP) Assessment Note: On the Proposed Project with Cambodia for REDD+ Readiness Preparation Support; Forest Carbon Partnership Facility: Phnom Penh, Cambodia, 2011. [Google Scholar]
  66. Shimizu, K.; Ota, T.; Onda, N.; Mizoue, N. Combining post-disturbance land cover and tree canopy cover from Landsat time series data for mapping deforestation, forest degradation, and recovery across Cambodia. Int. J. Digit. Earth 2022, 15, 832–852. [Google Scholar] [CrossRef]
  67. Grogan, K.; Pflugmacher, D.; Hostert, P.; Mertz, O.; Fensholt, R. Unravelling the link between global rubber price and tropical deforestation in Cambodia. Nat. Plants 2019, 5, 47–53. [Google Scholar] [CrossRef]
  68. Ken, S.; Sasaki, N.; Entani, T.; Ma, H.O.; Thuch, P.; Tsusaka, T.W. Assessment of the local perceptions on the drivers of deforestation and forest degradation, agents of drivers, and appropriate activities in Cambodia. Sustainability 2020, 12, 9987. [Google Scholar] [CrossRef]
  69. Food and Argiculture Organization. Sub-Decree No. 79 on Community Forestry Management. Available online: https://www.fao.org/faolex/results/details/en/c/LEX-FAOC081979/#:~:text=Cambodia-,Sub%2DDecree%20No.,is%20a%20State%20public%20property. (accessed on 3 March 2025).
  70. United Nations Office on Drugs and Crime. Law on Forestry 2002. Available online: https://sherloc.unodc.org/cld/document/khm/2002/law_on_forestry.html? (accessed on 3 March 2025).
  71. Forestry Administration. Community Forest Statistics 2023; Forestry Administration: Phnom Penh, Cambodia, 2023. [Google Scholar]
  72. Client Earth. Community Protected Areas in Cambodia: Analysis of Legal Framework, Practice and Recommendations; Client Earth: Brussels, Belgium, 2022. [Google Scholar]
  73. IWGIA. The Indigenous World 2024: Cambodia. Available online: https://iwgia.org/en/cambodia/5364-iw-2024-cambodia.html#:~:text=As%20of%202023%2C%20out%20of%20488%20Indigenous,two%20of%20which%20were%20approved%20in%202023 (accessed on 11 April 2025).
  74. IUCN. Sustainable Financing for Community Fisheries in Cambodia. Available online: https://iucn.org/story/202412/sustainable-financing-community-fisheries-cambodia#:~:text=Today%2C%20Community%20Fisheries%20in%20Cambodia,which%20447%20are%20officially%20registered. (accessed on 18 March 2025).
  75. Yeang, D.; Brewster, J. REDD+ Demonstration Activities in Cambodia: The Case of the Oddar Meanchey Community Forestry REDD+ Project; Forestsry Administration: Phnom Penh, Cambodia, 2012. [Google Scholar]
  76. Cambodia REDD+ Taskforce Secretariat. About REDD+. Available online: https://cambodia-redd.org/about-redd.html (accessed on 3 March 2025).
  77. Cambodia REDD+ Safeguards. REDD+ Secretariat. Available online: https://cambodia-redd.org/governance/secretariat.html (accessed on 3 March 2025).
  78. Nguon, P. “Full and Effective Participation” in the UNFCCC REDD+ Implementation in Cambodia. Available online: https://cy-onekhmer.com/wp-content/uploads/2017/12/12.-Cover-page.pdf (accessed on 16 July 2024).
  79. Cambodia REDD+ Safeguards. REDD+ Taskforce. Available online: https://cambodia-redd.org/governance/taskforce.html (accessed on 3 March 2025).
  80. Verra. Verified Carbon Standard. Available online: https://registry.verra.org/app/search/VCS (accessed on 3 March 2025).
  81. Aster Global. JCM Validation Report Form for REDD-Plus; Aster Global Environmental Solutions: North Lawrence, OH, USA, 2023. [Google Scholar]
  82. Global Environmental Centre Foundation. Overview of the Joint Crediting Mechanism (JCM). Available online: https://gec.jp/jcm/about/ (accessed on 3 March 2025).
  83. Cambodia REDD+ Taskforce Secretariat. Action & Investment Plan for the implementation of the National REDD+ Strategy of Cambodia. Available online: https://cambodia-redd.org/wp-content/uploads/2020/07/REDD-Action-Investment-Plan-Final-version-April-2020.pdf (accessed on 3 March 2025).
  84. REDD+ Taskforce Secretariat. First Summary of Information on Safeguards. Available online: https://redd.unfccc.int/media/6._cambodia_1st_summary_of_information_on_safeguards-final-oct-2019.pdf (accessed on 3 March 2025).
  85. Awuah, K.T. REDD+ and Opportunity for Biodiversity Conservation; University of Göttingen: Göttingen, Germany, 2016. [Google Scholar]
  86. Yeang, D.; Eam, S.; Sherchan, K.; Mckerrow, L. Local community participation in biodiversity monitoring and its implication for REDD+: A case study of Changkran Roy Community Forest in Cambodia. In Proceedings of the 7th International Conference on Environment and Rural Development, Phnon Penh, Cambodia, 16–17 January 2016. [Google Scholar]
  87. Gené, E.I.; Scheyvens, H.; López-Casero, F. Community forest management and REDD+: Opportunities and challenges. In IGES White Paper IV; Institute of Global Environmental Strategies: Hayama, Japan, 2012; pp. 85–114. [Google Scholar]
  88. Scheyvens, H.; Fujisaki, T.; Yamanoshita, M. Forestry: Importance of Local Participation in MRV of REDD; Institute for Global Environmental Strategies: Hayama, Japan, 2013. [Google Scholar]
  89. Theilade, I.; Holger, L. Redd+ and Conservation of Prey Long Forest, Cambodia. Summary of Scientific Findings 2007–2010; Forest & Landscape Denmark: Copenhagen, Denmark, 2011. [Google Scholar]
  90. Avtar, R.; Sawada, H.; Kumar, P. Role of remote sensing and community forestry to manage forests for the effective implementation of REDD+ mechanism: A case study on Cambodia. Environ. Dev. Sustain. 2013, 15, 1593–1603. [Google Scholar] [CrossRef]
  91. Pauly, M.; Tosteson, J. Safeguarding natural forests through the voluntary REDD+ scheme. Nat. Plants 2022, 8, 861–866. [Google Scholar] [CrossRef]
  92. Verra. Verified Carbon Standard: Project and Credit Summary. Available online: https://registry.verra.org/app/search/VCS/All%20Projects (accessed on 3 March 2025).
  93. Joint Crediting Mechanism. Project: KH005 Prey Lang Wildlife Sanctuary-Stung Treng REDD+ Project. Available online: https://www.jcm.go.jp/projects/92 (accessed on 12 May 2025).
  94. Khorn, N.; (Cambodian Forestry Administration, Phnom Penh, Cambodia). Personal communication, 20 November 2024.
  95. Kong, B.; (Conservation International, Phnom Penh, Cambodia). Personal communication, 2 December 2024.
  96. Vorn, S.; (Cambodian Ministry of Environment, Phnom Penh, Cambodia). Personal communication, 15 March 2024.
  97. Anderson, P. Free, Prior, and Informed Consent in REDD+: Principles and Approaches for Policy and Project Development; RECOFTC and GIZ: Bangkok, Thailand, 2011. [Google Scholar]
  98. Seth, K.; Ahmad, D.; Lok Mani, S.; David, G. Transforming forest landscape conflicts: The promises and perils of global forest management initiatives such as REDD+. For. Soc. 2018, 2, 1–17. [Google Scholar] [CrossRef]
  99. Filer, C.; Mahanty, S.; Potter, L. The FPIC Principle Meets Land Struggles in Cambodia, Indonesia and Papua New Guinea. Land 2020, 9, 67. [Google Scholar] [CrossRef]
  100. Milne, S.; Mahanty, S. Value and bureaucratic violence in the green economy. Geoforum 2019, 98, 133–143. [Google Scholar] [CrossRef]
  101. Frewer, T. What exactly do REDD+ projects produce? A materialist analysis of carbon offset production from a REDD+ project in Cambodia. Political Geogr. 2021, 91, 102480. [Google Scholar] [CrossRef]
  102. Work, C. Forest islands and castaway communities: REDD+ and forest restoration in Prey Lang Forest. Forests 2017, 8, 47. [Google Scholar] [CrossRef]
  103. Pasgaard, M.; Chea, L. Double inequity? The social dimensions of deforestation and forest protection in local communities in Northern Cambodia. Adv. Southeast Asian Stud. 2013, 6, 330–355. [Google Scholar] [CrossRef]
  104. Pasgaard, M.; Nielsen, T.F. A story of “communities”: Boundaries, geographical composition and social coherence in a forest conservation project, Northern Cambodia. Geogr. Tidsskr.-Dan. J. Geogr. 2016, 116, 134–146. [Google Scholar] [CrossRef]
  105. Bourdier, F. “Saving the Forest” with a REDD+ Project: Socio-Ecological Repercussions on Indigenous People in Cambodia. Qeios 2024. [Google Scholar] [CrossRef]
  106. Milne, S.; Adams, B. Market masquerades: Uncovering the politics of community-level payments for environmental services in Cambodia. Dev. Change 2012, 43, 133–158. [Google Scholar] [CrossRef]
  107. UNFCCC. Safeguards. Available online: https://redd.unfccc.int/fact-sheets/safeguards.html (accessed on 3 March 2025).
  108. Nguon, P. Co-production of salient, credible and legitimate environmental knowledge: Cambodia National REDD+ Strategy. Sustain. Sci. 2019, 14, 861–873. [Google Scholar] [CrossRef]
  109. UN-REDD. Grievance Redress Mechanism (GRM). Available online: https://www.un-redd.org/glossary/grievance-redress-mechanism-grm#:~:text=The%20formal%20and%20informal%20means,the%20implementation%20of%20REDD%2B%20activities (accessed on 3 March 2025).
  110. Verra. Verified Carbon Units (VCUs). Available online: https://verra.org/programs/verified-carbon-standard/verified-carbon-units-vcus/ (accessed on 3 March 2025).
  111. Persson, J.; Prowse, M. Collective action on forest governance: An institutional analysis of the Cambodian community forest system. For. Policy Econ. 2017, 83, 70–79. [Google Scholar] [CrossRef]
  112. Pasgaard, M. Lost in translation? How project actors shape REDD plus policy and outcomes in Cambodia. Asia Pac. Viewp. 2015, 56, 111–127. [Google Scholar] [CrossRef]
  113. Human Rights Watch. Carbon Offsetting’s Casualties Violations of Chong Indigenous People’s Rights in Cambodia’s Southern Cardamom REDD+ Project; Human Rights Watch: New York, NY, USA, 2024. [Google Scholar]
  114. Riggs, R.A.; Langston, J.D.; Beauchamp, E.; Travers, H.; Ken, S.; Margules, C. Examining Trajectories of Change for Prosperous Forest Landscapes in Cambodia. Environ. Manag. 2020, 66, 72–90. [Google Scholar] [CrossRef]
  115. Yeang, D. Community Tenure Rights and REDD+: A Review of the Oddar Meanchey Community Forestry REDD+ Project in Cambodia. Austrian J. Southeast Asian Stud. 2012, 5, 263–274. [Google Scholar] [CrossRef]
  116. Nhem, S.; Lee, Y.-j. Exploring perspectives in assessing the quality of governance of the Reducing Emissions from Deforestation and Forest Degradation (REDD+) pilot project in Cambodia: Use of Q Methodology. J. Mt. Sci. 2020, 17, 95–116. [Google Scholar] [CrossRef]
  117. Nathan, I.; Boon, T. Constraints and Options in Local Forest Management in Cambodia: Is Decentralization a Solution? J. Sustain. For. 2012, 31, 396–420. [Google Scholar] [CrossRef]
  118. Chapman, S.; Wilder, M.; Millar, I.; Dibley, A.; Yeang, D.; Heffernan, J.; Sherchan, K.; Maguire, R.; Kago, C.; Kamunde-Aquino, N.; et al. A legal perspective of carbon rights and benefit sharing under REDD+: A conceptual framework and examples from Cambodia and Kenya. Carbon Clim. Law Rev. 2015, 9, 143–155. [Google Scholar]
  119. Evans, T. Pilot REDD Activities in Cambodia are Expected to Improve Access to Forest Resource Use Rights and Land Tenure for Local Communities. In Lessons About Land Tenure, Forest Governance and REDD+. Case Studies from Africa, Asia and Latin America; Lisa Naughton-Treves, C.D., Ed.; Land Tenure Center, University of Wisconsin-Madison: Madison, WI, USA, 2012. [Google Scholar]
  120. Scheidel, A.; Work, C. Forest plantations and climate change discourses: New powers of ‘green’ grabbing in Cambodia. Land Use Policy 2018, 77, 9–18. [Google Scholar] [CrossRef]
  121. FAO. Forestry: Tenure Security for Better Forestry. Available online: https://www.fao.org/forestry/our-focus/forests-people/forest-tenure/en#:~:text=Forest%20tenure%20may%20be%20defined%20as%20the%20right,and%20under%20what%20conditions%20these%20rights%20are%20held. (accessed on 3 March 2025).
  122. CIFOR. Definitions: Forest tenure. Available online: https://www2.cifor.org/forest-tenure/about/definitions/ (accessed on 3 March 2025).
  123. Food and Agriculture Organization of the United Nations. Law on Forestry 2002. Available online: https://www.fao.org/faolex/results/details/en/c/LEX-FAOC050411/ (accessed on 3 March 2025).
  124. Yeang, D. Tenure Rights and Benefit Sharing Arrangements for REDD: A Case Study of Two REDD Pilot Projects in Cambodia; Wageningen University: Wageningen, The Netherlands, 2010. [Google Scholar]
  125. Milne, S. Grounding Forest Carbon: Property Relations and Avoided Deforestation in Cambodia. Hum. Ecol. 2012, 40, 693–706. [Google Scholar] [CrossRef]
  126. Mahanty, S.; Milne, S.; Dressler, W.; Filer, C. The Social Life of Forest Carbon: Property and Politics in the Production of a New Commodity. Hum. Ecol. Interdiscip. J. 2012, 40, 661–664. [Google Scholar] [CrossRef]
  127. Ian, G.B. Reduced Emissions from Deforestation and Forest Degradation (REDD) and Access and Exclusion: Obstacles and Opportunities in Cambodia and Laos. Southeast Asian Stud. 2014, 3, 643–668. [Google Scholar] [CrossRef]
  128. UN-REDD. Forest Tenure, Governance and Carbon Rights. Available online: https://www.un-redd.org/work-areas/forest-tenure-governance-carbon-rights (accessed on 3 March 2025).
  129. Forestry Administration. Reports and Publication. Available online: http://tumringredd.org/report-and-publication/ (accessed on 3 March 2025).
  130. Washington, H. Keo Seima Wildlife Sanctuary REDD+: Benefit-Sharing Manual; Wildlife Conservation Society: Phnom Penh, Cambodia, 2022. [Google Scholar]
  131. Yin, S.; Vang, S. Payment for Ecosystem Services in Cambodia: Challenges and Potential. In Water and Power: Environmental Governance and Strategies for Sustainability in the Lower Mekong Basin; Stewart, M.A., Coclanis, P.A., Eds.; Springer International Publishing: Cham, Switzerland, 2019; pp. 115–122. [Google Scholar] [CrossRef]
  132. Post, D. CDD and Elite Capture: Reframing the Conversation; World Bank: Washington, DC, USA, 2008. [Google Scholar]
  133. Nhem, S.; Lee, Y.J. Using Q methodology to investigate the views of local experts on the sustainability of community-based forestry in Oddar Meanchey province, Cambodia. For. Policy Econ. 2019, 106, 101961. [Google Scholar] [CrossRef]
  134. FAO; MRLG. Challenges and Opportunities of Recognizing and Protecting Custormary Tenure Systems in Cambodia; FAO: Bangkok, Thailand, 2019. [Google Scholar]
  135. Nathan, I.; Pasgaard, M. Is REDD plus effective, efficient, and equitable? Learning from a REDD plus project in Northern Cambodia. Geoforum 2017, 83, 26–38. [Google Scholar] [CrossRef]
  136. Milne, S.; Chervier, C. A Review of Payments for Environmental Services (PES) Experiences in Cambodia; CIFOR: Bogor, Indonesia, 2014. [Google Scholar]
  137. Yeang, D.; Reyes, L.G.; Un, E.S. Policy Brief: Carbon Rights and Benefit Sharing in Cambodia, European Union Cambodia; Ecologic Institute: Phnom Penh, Cambodia, 2014. [Google Scholar]
  138. Maraseni, T.N.; Poudyal, B.H.; Rana, E.; Chandra Khanal, S.; Ghimire, P.L.; Subedi, B.P. Mapping national REDD+ initiatives in the Asia-Pacific region. J. Environ. Manag. 2020, 269, 110763. [Google Scholar] [CrossRef]
  139. Ken, S.; Entani, T.; Tsusaka, T.W.; Sasaki, N. Effect of REDD+ projects on local livelihood assets in Keo Seima and Oddar Meanchey, Cambodia. Heliyon 2020, 6, e03802. [Google Scholar] [CrossRef] [PubMed]
  140. Yeang, D.; Washington, H.; Sereyrotha, K.; Choup, P.; Silverman, J.; Rithiny, T.; Mahood, S. REDD+ in Cambodia: How local communities can benefit from forest conservation. Cambodian J. Nat. Hist. 2018, 2, 53–55. [Google Scholar]
  141. Thompson, B.S. Can Financial Technology Innovate Benefit Distribution in Payments for Ecosystem Services and REDD+? Ecol. Econ. 2017, 139, 150–157. [Google Scholar] [CrossRef]
  142. World Economic Forum. How the Voluntary Carbon Market Could Help Us Get to Net Zero. Available online: https://www.weforum.org/agenda/2022/03/voluntary-carbon-market-net-zero/ (accessed on 3 March 2025).
  143. Ra, K.; Sasaki, N. Assessment of local livelihood of forest-dependent communities in Cambodia. Int. J. Environ. Rural Dev. 2013, 4, 63–68. [Google Scholar] [CrossRef]
  144. Milbank, C.; Coomes, D.; Vira, B. Assessing the Progress of REDD+ Projects towards the Sustainable Development Goals. Forests 2018, 9, 589. [Google Scholar] [CrossRef]
  145. WCS. Keo Seima REDD+. Available online: https://cambodia.wcs.org/Keo-Seima-REDD.aspx#:~:text=Keo%20Seima%20REDD%2B%20offers%20a%20transformative%20and%20sustainable,challenges%20of%20our%20time%3A%20protecting%20threatened%20forest%20ecosystems (accessed on 3 March 2025).
  146. Wildlife Alliance. Livelihoods and Communities. Available online: https://www.wildlifealliance.org/livelihoods/ (accessed on 3 March 2025).
  147. Scoones, I. Sustainable Rural Livelihoods: A Framework for Analysis; Institute of Development Studies Brighton: Brighton, UK, 1998. [Google Scholar]
  148. AFOCO. Towards Afforestation, Adaptation to Climate Change, and Non-Formal Economic Development in Cambodia: Customized Forest Models Through Tree Plantations and Agroforestry Practices of Local Communities. Available online: https://afocosec.org/newsroom/news/stories/towards-afforestation-adaptation-to-climate-change-and-non-formal-economic-development-in-cambodia-customized-forestation-models-through-tree-plantations-and-agroforestry-practices-of-local-communi/ (accessed on 3 March 2025).
  149. NTFP-EP. Agroforestry Project. Available online: http://ntfp.org.kh/?page_id=598 (accessed on 3 March 2025).
  150. The World Bank Group. Cambodia: Country Climate and Development Report; The World Bank Group: Washington, DC, USA, 2023. [Google Scholar]
  151. Mulcahy, G.; Boissière, M. No Forest, no NTFPs for Rural Communities in Cambodia; CIFOR: Bogor, Indonesia, 2014. [Google Scholar]
  152. Oxfam. New Regulation on Community Saving Groups in Cambodia. Available online: https://cambodia.oxfam.org/new-regulation-community-saving-groups-cambodia (accessed on 3 March 2025).
  153. RECOFTC. Credit Scheme Boosts Livelihoods in Cambodia. Available online: https://www.recoftc.org/recoftc-annual-report-2019-2020/credit-scheme-boosts-livelihoods-cambodia (accessed on 3 March 2025).
  154. UNDP. Forest Carbon Partnership Facility REDD+ Readiness Project Phase II (FCPF-II). Available online: https://www.undp.org/cambodia/projects/forest-carbon-partnership-facility-redd-readiness-project-phase-ii-fcpf-ii (accessed on 3 March 2025).
  155. UNDP. UK Government Supports to Cambodia National REDD+ Programme Implementation Through Climate Promise 2.0. Available online: https://www.undp.org/cambodia/speeches/uk-government-supports-cambodia-national-redd-programme-implementation-through-climate-promise-20 (accessed on 3 March 2025).
  156. Nop, S. Climate Change Adaptation in Cambodia. In Climate Change Adaptation in Southeast Asia; Pereira, J.J., Zain, M.K., Shaw, R., Eds.; Springer Singapore: Singapore, 2022; pp. 43–56. [Google Scholar] [CrossRef]
  157. Chhun, D.; Nguon, P. Safeguards and SIS: Cambodia. Available online: https://www.un-redd.org/sites/default/files/2021-10/Cambodia-Summary%20of%20Country%20Safeguards-th.pdf (accessed on 3 March 2025).
  158. Somanta, C.; Nophea, S.; Hiroshi, N. Carbon emission reductions by substitution of improved cookstoves and cattle mosquito nets in a forest-dependent community. Glob. Ecol. Conserv. 2015, 4, 434–444. [Google Scholar] [CrossRef]
  159. UN-REDD. Community-Based REDD+. Available online: https://www.un-redd.org/projects/community-based-redd (accessed on 9 November 2024).
  160. Beang, L.C.; Sethaphal, L. Community Forestry in Cambodia. Available online: https://www.fao.org/4/ad511e/ad511e0a.htm#:~:text=HISTORY%20OF%20COMMUNITY%20FORESTRY&text=Community%20forestry%20initiatives%20have%20been,Pursat%20and%20Siem%20Reap%20Provinces (accessed on 3 February 2025).
  161. Asian Development Bank. Climate Risk Country Profile: Cambodia. Available online: https://www.adb.org/publications/climate-risk-country-profile-cambodia (accessed on 3 March 2025).
  162. Neef, A.; Boruff, B.; Bruce, E.; Ngin, C.; Pauli, N.; Davies, K.; van Ogtrop, F.; Varea, R.; Weber, E. Climate change adaptation in disaster-prone communities in Cambodia and Fiji. APN Sci. Bull. 2020, 10, 67–75. [Google Scholar] [CrossRef]
  163. Sapkota, L.M.; Silori, C.S.; Dangal, S.P.; Than, M.M.; Sokchea, T.; Chhneang, K.; Thu, A.K.; Van Chau, T.; Katwal, N. Beyond the Biophysical: Contribution of Community Forestry in Building Social-Ecological Resilience. In Forest Dynamics and Conservation: Science, Innovations and Policies; Kumar, M., Dhyani, S., Kalra, N., Eds.; Springer Nature Singapore: Singapore, 2022; pp. 187–211. [Google Scholar] [CrossRef]
  164. Poffenberger, M. People in the forest: Community forestry experiences from Southeast Asia. People For. Community For. Exp. Southeast Asia 2006, 5, 57–69. [Google Scholar] [CrossRef]
  165. Agyei, K. The Implications of Land Tenure and Benefit Sharing Approaches on the REDD+ Scheme for Forest Fringe Communities in Ghana; Australian National University: Sydney, Australia, 2012. [Google Scholar]
  166. Andersson, K.; Smith, S.M.; Alston, L.J.; Duchelle, A.E.; Mwangi, E.; Larson, A.M.; de Sassi, C.; Sills, E.O.; Sunderlin, W.D.; Wong, G. Wealth and the distribution of benefits from tropical forests: Implications for REDD+. Land Use Policy 2018, 72, 510–522. [Google Scholar] [CrossRef]
  167. McElwee, P.; Nguyen, V.; Nguyễn, D.; Trần, N.; Le, H.; Nghiêm, T.; Vũ, H. Using REDD+ Policy to Facilitate Climate Adaptation at the Local Level: Synergies and Challenges in Vietnam. Forests 2016, 8, 11. [Google Scholar] [CrossRef]
  168. Sawathvong, S.; Hyakumura, K. A Comparison of the Free, Prior, and Informed Consent (FPIC) Guidelines and the “Implementation of Governance, Forest Landscapes, and Livelihoods” Project in Lao PDR: The FPIC Team Composition and the Implementation Process. Land 2024, 13, 408. [Google Scholar] [CrossRef]
  169. Sawathvong, S.; Hyakumura, K.; Fujisaki, T. Stakeholder Participation in REDD+ Program: The Case of the Consultation Process in Laos. Land 2024, 13, 1137. [Google Scholar] [CrossRef]
  170. Tebkew, M.; Atinkut, H.B. Impact of forest decentralization on sustainable forest management and livelihoods in East Africa. Trees For. People 2022, 10, 100346. [Google Scholar] [CrossRef]
  171. Dieng, M.; Mbow, C.; Skole, D.; Ba, B. Sustainable land management policy to address land degradation: Linking old forest management practices in Senegal with new REDD+ requirements. Front. Environ. Sci. 2023, 11, 1088726. [Google Scholar] [CrossRef]
  172. Lozano Flores, L.; Delgado Pugley, D.; Casas Luna, S.; Van den Broeck, P.; Parra, C. Challenging state authority and hierarchical power: A case study of the engagement of Peru’s Amazonian Indigenous Peoples’ organizations in the governance of REDD+. Environ. Policy Gov. 2024, 34, 137–151. [Google Scholar] [CrossRef]
  173. Tiki, L.; Marquardt, K.; Abdallah, J.M. Participatory forest management: Analysis of local forest governance and implications for REDD+ implementation in the Adaba-Dodola Forest in Ethiopia. Trees For. People 2025, 19, 100780. [Google Scholar] [CrossRef]
  174. Aryal, K.; Maraseni, T.; Subedi, B.P.; Laudari, H.K.; Ghimire, P.L.; Khanal, S.C.; Zhang, H.; Timilsina, R. REDD+ at risk: Emerging ten questions that REDD+ must answer. Environ. Sci. Policy 2024, 156, 103744. [Google Scholar] [CrossRef]
  175. Nantongo, M.; Vatn, A.; Soka, G. REDD+: The perfect marriage between conservation and development? A comparative study of the impacts of REDD+ on livelihoods and deforestation in Tanzania. World Dev. 2024, 173, 106432. [Google Scholar] [CrossRef]
  176. Gauthier, M. Re-territorializing climate governance: The REDD+ initiatives in the DR Congo. Fourth World J. 2024, 24, 91–109. [Google Scholar] [CrossRef]
  177. Chorito, A.B.; Assefa, E. Actors participation and power relations of REDD+ implementation in Bale Eco Region, Ethiopia. Clim. Policy 2024, 24, 1065–1079. [Google Scholar] [CrossRef]
  178. Osborne, T.; Cifuentes, S.; Dev, L.; Howard, S.; Marchi, E.; Withey, L.; Santos Rocha da Silva, M. Climate justice, forests, and Indigenous Peoples: Toward an alternative to REDD + for the Amazon. Clim. Chang. 2024, 177, 128. [Google Scholar] [CrossRef]
  179. Osei, M.K. Exploring System Context Contributing to Emerging REDD+ Collaborative Governance Regime in Ghana: Stakeholders Perceptions at the National Level. Environ. Manag. 2024, 75, 505–523. [Google Scholar] [CrossRef]
  180. Sunderlin, W.D.; Atmadja, S.S.; Chervier, C.; Komalasari, M.; Resosudarmo, I.A.P.; Sills, E.O. Can REDD+ succeed? Occurrence and influence of various combinations of interventions in subnational initiatives. Glob. Environ. Chang. 2024, 84, 102777. [Google Scholar] [CrossRef]
  181. Vijitharan, S.; Tsusaka, T.W.; Sasaki, N. Evaluating REDD+ progress and results-based incentives in Sri Lanka: A comparative analysis across Southeast and South Asian countries. Trees For. People 2024, 16, 100574. [Google Scholar] [CrossRef]
  182. Lord, E.J. Fragmenting forest governance: Land tenure and the REDD+ paradox in Kigoma pilot project, Tanzania. Political Geogr. 2025, 116, 103234. [Google Scholar] [CrossRef]
  183. Duchelle, A.E.; Cromberg, M.; Gebara, M.F.; Guerra, R.; Melo, T.; Larson, A.M.; Cronkleton, P.; Börner, J.; Sills, E.O.; Wunder, S.; et al. Linking forest tenure reform, environmental compliance, and incentives: Lessons from REDD+ initiatives in the Brazilian Amazon. World Dev. 2014, 55, 53–67. [Google Scholar] [CrossRef]
  184. Atela, J.O.; Minang, P.A.; Quinn, C.H.; Duguma, L.A. Implementing REDD+ at the local level: Assessing the key enablers for credible mitigation and sustainable livelihood outcomes. J. Environ. Manag. 2015, 157, 238–249. [Google Scholar] [CrossRef]
  185. Shah, S.; Race, D. Greening the blue Pacific: Lessons on reducing emissions from deforestation and forest degradation (REDD+). For. Policy Econ. 2024, 166, 103263. [Google Scholar] [CrossRef]
  186. Aryal, K.; Maraseni, T.; Rana, E.; Subedi, B.P.; Laudari, H.K.; Ghimire, P.L.; Khanal, S.C.; Zhang, H.; Timilsina, R. Carbon emission reduction initiatives: Lessons from the REDD+ process of the Asia and Pacific region. Land Use Policy 2024, 146, 107321. [Google Scholar] [CrossRef]
  187. Dugasseh, F.A.; Adams, M.A.; Zandersen, M. Actor Perceptions of the Governance Framework and Non-Carbon Benefits from the Ghana Cocoa Forest REDD+ Program: An Extended Q-Study of the Juabuso-Bia Hotspot Intervention Area. Environ. Manag. 2024, 74, 73–93. [Google Scholar] [CrossRef] [PubMed]
  188. Wahyudi, R.; Marjaka, W.; Silangen, C.; Fajar, M.; Dharmawan, I.W.S.; Mariamah. Effectiveness, efficiency, and equity in jurisdictional REDD+ benefit distribution mechanisms: Insights from Jambi province, Indonesia. Trees For. People 2024, 18, 100726. [Google Scholar] [CrossRef]
  189. Kumar, M.; Nisha Phukon, S.; Singh, H. Chapter 24—The role of communities in sustainable land and forest management. In Forest Resources Resilience and Conflicts; Kumar Shit, P., Pourghasemi, H.R., Adhikary, P.P., Bhunia, G.S., Sati, V.P., Eds.; Elsevier: Amsterdam, The Netherlands, 2021; pp. 305–318. [Google Scholar] [CrossRef]
  190. Atela, J.O.; Quinn, C.H.; Minang, P.A. Are REDD projects pro-poor in their spatial targeting? Evidence from Kenya. Appl. Geogr. 2014, 52, 14–24. [Google Scholar] [CrossRef]
  191. Paris, T. A Study of How REDD+ Can Be Used to Improve the Adaptation of Local Communities to Climate Change—A Case Study of Central Kalimantan Indonesia; University of Queensland: Brisbane, Australia, 2016. [Google Scholar]
Figure 1. Locations of REDD+ projects in Cambodia.
Figure 1. Locations of REDD+ projects in Cambodia.
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Figure 2. REDD+ project revenue distribution in Cambodia.
Figure 2. REDD+ project revenue distribution in Cambodia.
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Table 1. Types of community forest management in Cambodia.
Table 1. Types of community forest management in Cambodia.
CFMDescriptionNumber and Size
Community ForestsThe Cambodian Forestry Law 2007 and Sub-decree No. 79 2003 provide the legal structure for rural communities to participate in forest management through community forestry in forest areas they have traditionally utilized [69,70].As of 2023, there are 648 CFs, covering 528,340 hectares [71].
Community Protected AreasCPAs are establishments based on the Guideline on Procedure and Process of Community Protected Area Establishment 2017, issued by the Ministry of Environment. They are areas traditionally managed by communities in the community zone of protected areas [72].As of 2022, there are 182 CPAs, covering 309,463 hectares [72].
Indigenous Community Land TitlingICLT is a land titling program developed by the Cambodian Government with support from development partners, aiming to help indigenous communities to formally register with the Ministry of Interior in accordance with the Land Law 2001 and the Sub-decree on Procedures for Registering of Land of Indigenous Communities 2009 [11].As of 2022, 40 of Cambodia’s 488 indigenous communities have obtained collective land titles [73].
Community FisheriesDefined by the Fisheries Law 2006 and the Sub-decree on Community Fisheries Management 2007, CFis are fishing domains including mangroves and flooded forests controlled by the state and handed over to communities, who live in and/or around the fishing domain, depend on it for their daily life, and use traditional fishing methods [74].As of 2023, there are 516 CFis [74].
Table 2. Key social safeguards in Cambodia’s First Summary of Information on Safeguards [84].
Table 2. Key social safeguards in Cambodia’s First Summary of Information on Safeguards [84].
Safeguard Clarification of the Cancun Safeguards in Accordance with the Country Context Core Elements Recognized and Protected in the Implementation of the REDD+ Strategy
Safeguard BThe rights of access to information, accountability, justice, gender equality, land tenure, and fair distribution of benefits will be clarified, respected, and promoted in the application of the National REDD+ Strategy.
  • Right to access information.
  • Right to access justice.
  • User rights over forest land (particularly for indigenous peoples and women).
  • Fair distribution of benefits.
Safeguard CThe REDD+ Strategy will be implemented in accordance with recognition of, and respect for, the rights of indigenous peoples and local communities, including the rights to non-discrimination, traditional knowledge and culture, self-determination, benefit-sharing, and collective tenure rights.
  • The rights of indigenous peoples, local communities, and women.
  • Traditional knowledge.
Safeguard DThe right to participate in an effective manner, including free, prior, and informed consent for relevant indigenous peoples and local communities, will be recognized and promoted under the implementation of the REDD+ Strategy.
  • The rights of indigenous peoples and local communities, especially women, to participate in implementation of policies and measures.
  • Right to free, prior, and informed consent.
Table 3. REDD+ projects in Cambodia.
Table 3. REDD+ projects in Cambodia.
No.REDD+ ProjectNo. of VillagesNo. of FamiliesNo. of
CFs
No. of CPAsNo. of ICLTNo. of
CFis
Project IDSize (ha)Estimated Annual Emission Reduction (Tons CO2e)Crediting PeriodSource
1Oddar Meanchey 58991513---90463,831204,7922008–2038[92]
2Keo Seima 172552-0715-1650166,9831,426,6482010–2069[92]
3Tumring 19325216---168967,791378,4342015–2044[92]
4Southern Cardamom21247514---1748465,8393,867,5682015–2044[92]
5Samkos 22304106---3341282,7181,549,3412019–2049[92]
6Lomphat 327308-03--3434134,730239,7522018–2047[92]
7Prey Lang 4913,118031603-KH005431,683327,6532018–2029[93]
8Mangrove Afforestation and Reforestation -----135071300028,6502025–2045[92]
9Mekong 24-14----30,526215,549-[94]
10Central Cardamom 223296010617--401,313-2021–2051[95]
11Phnom Thnoat Phnom Pok * 42,097 [96]
12Northern Plain * 518,130 [96]
* No data are currently available for these projects.
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Y, C.; Hytten, K.F.; Pearson, D. Community Forest Management and REDD+: Pathways to Effective Implementation, Livelihood Improvement, and Climate Change Adaptation in Cambodia. Land 2025, 14, 1122. https://doi.org/10.3390/land14051122

AMA Style

Y C, Hytten KF, Pearson D. Community Forest Management and REDD+: Pathways to Effective Implementation, Livelihood Improvement, and Climate Change Adaptation in Cambodia. Land. 2025; 14(5):1122. https://doi.org/10.3390/land14051122

Chicago/Turabian Style

Y, Chaly, Karen F. Hytten, and Diane Pearson. 2025. "Community Forest Management and REDD+: Pathways to Effective Implementation, Livelihood Improvement, and Climate Change Adaptation in Cambodia" Land 14, no. 5: 1122. https://doi.org/10.3390/land14051122

APA Style

Y, C., Hytten, K. F., & Pearson, D. (2025). Community Forest Management and REDD+: Pathways to Effective Implementation, Livelihood Improvement, and Climate Change Adaptation in Cambodia. Land, 14(5), 1122. https://doi.org/10.3390/land14051122

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