Community forestry is a participatory model of forestry that gained prominence in the 1970s in which local communities take an active role in forest management and land use decision making. Community forestry is defined by the Food and Agricultural Organization of the United Nations as "any situation that intimately involves local people in forestry activity". [1] Unlike centralized management systems, community forestry more strongly emphasizes the participation and collaboration of local community stakeholders, along with government and non-governmental organizations (NGOs). The level of involvement of each of these groups is dependent on the specific community forest project, the management system and the region.
Examples of community forestry have existed throughout history and exist today across South Asia, Africa, Latin America, and parts of Europe, often integrating traditional ecological knowledge with modern management. These initiatives are recognized for their contributions to climate resilience, forest regeneration, and socio-economic development. [2] [3] Many projects aim to protect community livelihoods, enhance resource access, reduce poverty, or promote sustainable land management, however, these initiatives can face many challenges in practice.
Community forestry is a branch of forestry that deals with the communal management of forests for generating income from timber and non-timber forest products on one hand, and managing for ecosystem services such as watershed conservation, carbon sequestration and aesthetic values on the other hand. It has been considered one of the most promising options of combining forest conservation with rural development, community empowerment and poverty reduction objectives.
The concept of community forestry first came to prominence in the mid-1970s but is rooted in historical land management systems that prioritized collective stewardship. For example, in pre-colonial Africa, community-managed forests served as critical sources of food, medicine, and cultural heritage, governed through traditional norms and local leadership structures. [4] Similarly, before enclosure or other land privatization efforts, European commons allowed communities to access forests for grazing, fuelwood, and construction materials under shared use. Around the world, colonial governance and widespread land privatization disrupted these practices by replacing communal systems with centralized or private control. In regions such as India, colonial forestry policies prioritized timber extraction and commercial gains, often displacing indigenous communities and undermining traditional knowledge. This widespread alienation of local populations from forest resources led to widespread degradation and social unrest, prompting calls for reform in Africa and other continents. [5]
The re-emergence of community forestry in the 20th century was driven by growing recognition of the ecological and social failures of centralized forest policy efforts. [6] Early movements, such as India’s Joint Forest Management in the 1970s and Nepal’s Forest User Groups in the 1980s, attempted to improve the management of forest resources and address environmental issues due to the countries failing centralized forest policy. [7] These early efforts illustrated the potential of participatory governance to address resource depletion and empower marginalized communities. In 1978, FAO’s seminal work, Forestry for Local Community Development, laid the foundation for integrating scientific forestry with traditional practices in the modern period, arguing that empowering local communities not only conserved resources but also improved socio-economic outcomes. [1] More recently, in the past few decades, community forestry has been implemented in developing countries and has been modestly successful in its aims of sustainable forest management, climate change adaptation, and securing socio-economic benefits for local communities. [8]
However, a study by the Overseas Development Institute has shown that the technical, managerial and financial requirements stipulated by community forestry frameworks are often incompatible with local realities and interests. A successful legal and institutional framework must incorporate the strengthening of existing institutions and enable the dissemination of locally appropriate practices as well as the local capacity for regulation and control. [9] In practice, successful models have combined adaptive management with community-driven initiatives. For example, Mexico’s community forest enterprises (CFEs) demonstrated that decentralized governance could generate substantial economic benefits while maintaining ecological integrity. Similarly, Nepal’s participatory forest management made progress in reducing poverty and restoring forest cover. [7] [10]
As of 2016, FAO estimated that almost one-third of the world's forest area is under some form of community-based management. [3]
Governance in community forestry emphasizes decentralization and participatory decision-making. Models such as Nepal’s Forest User Groups show how local empowerment can lead to improved conservation outcomes and equitable resource distribution. These groups operate democratically, with elected committees overseeing forest management, benefit-sharing, and conflict resolution. [7]
Other governance systems include co-management frameworks, as seen in Brazil’s Amazon. These systems involve partnerships between local communities, NGOs, and government agencies to balance conservation goals with socio-economic development. However, successful governance requires transparent processes, capacity-building, and mechanisms to address power imbalances between partners. [11]
Land tenure is a fundamental aspect of community forestry, affecting whether communities have the rights and security to invest in sustainable practices. In Mozambique, community forestry laws have helped formalize tenure arrangements, enabling local groups to manage forests and participate in carbon trading markets. However, challenges such as unclear boundaries, elite capture, and weak enforcement persist in many land tenure systems, threatening the viability of community forestry projects and creating uncertainty in terms of resource access. [12]
The history of informal land tenure systems and land privatization must be addressed for community forestry projects to be successful. In Latin America, Mexico’s ejido system provides a notable example of how collective tenure arrangements can support long-term resource management and economic development. By granting legal recognition to community-managed lands, the system fosters stability and investment in sustainable forestry. [10]
Sustainability in community forestry involves balancing ecological, social, and economic goals. Effective initiatives incorporate biodiversity conservation, sustainable harvesting practices, and equitable benefit-sharing. For example, Nepal’s community forestry programs have successfully regenerated forest areas while supporting local livelihoods, demonstrating resilience in the face of environmental and economic challenges. [2] Projects like Mozambique’s carbon forestry initiatives also highlight the role of community forestry in enhancing resilience to climate change by promoting afforestation and reforestation efforts. [13]
There are a large variety of stakeholders involved in community forestry. Stakeholders of community forestry have a vested interest in establishing sustainable practices, whether this be to develop and maintain a regular income, ensure that forests are sufficiently protected to ensure their longevity and reduce illegal activities, or to manage the area in such a way to promote tourism and conservation. Participation by stakeholders from the community, government and non-governmental organizations (NGOs) is essential in a project's success.
Communities are central to community forestry, with their participation ensuring that management practices reflect local priorities. Communities may have local or indigenous knowledge that can positively influence the stewardship of forest ecosystems and resources. Interestingly, faith communities are increasingly participating in efforts to promote ecological sustainability. [ citation needed ]
Whereas the last 50–100 years have seen faith communities lease out their territory to industry, they are beginning to reclaim and restore their land. There have been several highly successful efforts across Cambodia, which have been extended to Vietnam and Laos. [14] In September 2010, Buddhists monks were awarded the UNDP's Equator Prize for their ongoing conservation work. [15] This comprises the establishment of tree nurseries, seedling distribution, ordination activities, composting schemes and a vegetable garden, which is used to promote sustainable living and conservation. The site has become a valuable source of information and environmental education as well as a base for the local community. Villagers regularly hold panel discussions about how they can go on to best take advantage of what the natural forest has to offer without destroying it.[ citation needed ]
Governments provide essential legal frameworks and resources for community forestry. For example, Indonesia’s Hutan Desa program enables communities to manage forests under state supervision, promoting conservation while addressing rural poverty. However, institutional weaknesses, such as bureaucratic delays and limited capacity, often hinder implementation. [16]
NGOs and international organizations play a vital role in advocating for community rights and providing technical support. For example, in the Philippines, NGO-facilitated projects have empowered communities to restore degraded lands while generating income through agroforestry and ecotourism. [17] FAO’s work in documenting and disseminating best practices has also been instrumental in shaping global policy and capacity-building efforts. [3]
While specific stakeholders vary between different community forestry projects common stakeholder groups are summarized in the following table.
Local community |
---|
Communities living adjacent to or within the forest |
Traditional leaderships including village chief, elderly, clan heads, and spiritual leaderships |
Community-based organisations including forest users groups, networks of inter-villages forest protection, etc. |
Community representatives, local councils |
Government |
State government |
National government |
Departments of Agriculture, Forestry, Environment, etc. (specific to country and/or region) |
NGOs |
Environmental/conservation groups |
Commercial forestry industries |
Industries reliant on forests (i.e., harvestable products other than wood such as game meat) |
Tourism industry |
Animal welfare groups |
Natural ecosystem |
While the natural ecosystem does not have the same ability to articulate or communicate vested interests, it is possible to include the natural ecosystem as a stakeholder, conceptualizing ecosystem health, function, and longevity as some of its vested interests. [ citation needed ]
Due to differing complex regional socio-economic and environmental contexts, there is no blueprint management plan for community forestry projects. However, some variables have been observed to affect the success of community forest management systems, grouped by one study into the following five categories:
It has also been suggested that community conflict within community forest management may also be mitigated by the following approach:
Adaptive management has also been emphasized in community forestry literature. Participatory governance frameworks, such as Mexico’s CFEs, Nepal’s Forest User Groups, and Portugal's community forest management practices demonstrate how adaptive management can address diverse ecological and socio-economic needs. These models emphasize inclusivity, transparency, and accountability, fostering long-term success. [10] [21]
Incentives play a crucial role in encouraging communities to participate in and sustain forestry initiatives. They can be broadly categorized into those focused on household use and those aimed at developing market-oriented forestry.
Household use incentives can include the following.
Forestry can take on the character of agricultural production where there is a market for wood products such as poles, fuel wood and, pulp for production of paper, or where there is a market for non-timber forest products.
Aligning household and market incentives is central to community forestry management systems, and has potential to foster economic growth, ecological sustainability, and social cohesion.
Community forestry has been recognized for its potential to generate profound socio-economic benefits, particularly for marginalized, forest-dependent populations. By granting communities access and rights to forest resources, it creates opportunities for employment, income generation, and poverty alleviation.
In Nepal, Forest User Groups have enabled equitable benefit-sharing, ensuring that marginalized groups, such as women and lower-caste individuals, gain access to forest-derived incomes. These groups often reinvest revenues into community infrastructure, such as schools, water systems, and renewable energy projects, fostering broader socio-economic development. [7]
In Mexico, community forest enterprises (CFEs) not only generate significant economic returns through timber production but also invest in local job creation, housing, and education programs. These enterprises demonstrate how sustainable resource use can contribute to regional economic stability and resilience. [10] [25]
In the Philippines, community-managed agroforestry projects have helped restore degraded lands while providing communities with steady incomes from crops such as coffee, cacao, and fruits. These initiatives illustrate the potential of integrating forestry with agricultural livelihoods. [17]
Community forestry also contributes to global environmental goals including reducing deforestation, enhancing biodiversity, and promoting carbon sequestration. Reforestation initiatives in Nepal have reversed decades of forest loss, with some regions witnessing a 37% increase in forest cover under community management. [7]
In Africa, Mozambique’s community forestry initiatives play a dual role in biodiversity conservation and climate change mitigation. By participating in carbon trading schemes, communities gain financial incentives to conserve forests, thereby reducing emissions from deforestation. [13]
Latin America offers further evidence of environmental success, with Brazil’s co-managed forests in the Amazon acting as biodiversity hotspots while supporting sustainable livelihoods. These systems integrate local ecological knowledge with scientific management to enhance resilience against climate change and forest degradation. [11]
Research suggests that there are still major challenges for community forestry in practice. [2] Some of the major challenges are outlined below.
Governance challenges, such as bureaucratic inefficiency and lack of institutional capacity, often hinder the success of community forestry initiatives. In Mozambique, for instance, weak government oversight has led to inequitable benefit-sharing and insufficient support for capacity-building among local communities. [12]
Additionally, existing power imbalances between community members, local elites, and external stakeholders can unintentionally be exacerbated by community forestry initiatives. For example, in the Amazon, co-management efforts have faced criticism for failing to adequately represent marginalized groups, such as women and indigenous populations, in decision-making processes. [11]
Tenure insecurity remains a critical obstacle in community forestry. Unclear boundaries, competing claims, and weak enforcement mechanisms can undermine the claims to ownership or management rights of local communities, leading to conflicts and resource overexploitation.
In regions like sub-Saharan Africa, tenure systems often lack legal recognition, exposing communities to risks of land commodification and privatization. For example, land grabs by private entities in Mozambique have displaced local communities, limiting their ability to engage in sustainable forestry. [4] [12]
To address these challenges, experts advocate for legal reforms that prioritize tenure security, enhance community rights, and establish conflict-resolution mechanisms. [20]
Market-based mechanisms, such as certification systems or carbon credit projects, have enabled communities to access global markets for sustainable forest products or carbon sequestration. However, challenges such as high certification costs and limited market access remain barriers for smallholders. [24] [13]
A study conducted in the Brazilian Amazon determined that there are a number of challenges that must be faced when developing a sustainable management strategy for community forestry. These challenges are outlined below. The study's model is segregated into two phases: the development phase during which several enabling factors (land ownership, organizational capacity, technical knowledge and capital) are needed to obtain a legal management permit and secondly the operational phase where factors (clandestine loggers, access to markets, infrastructure and managerial skills) influence the success of the management program. [11] Each of the challenges outlined must be addressed in order for a self-sustaining community forestry management program to be established.
Issue | Description |
---|---|
Land ownership | It is not uncommon for small settlements living traditionally to lack clear title to the forests and lands, as such their rights to harvest the land may come into dispute. Formal recognition of land ownership or rights to use is needed for legal forest management. In Nepal, there is still confusion to communities about their tenure into services such as income from trading of carbon sequestration come from forestry resources. Government wants to hold revenue raised from trading of carbon but communities claim that it is our property due to be managed by us.[ who? ] |
Organizational capacity | Organizational capacity refers to the community's competence to organize a forest management program. |
Capital | A community will require start-up capital to invest in the required infrastructure, equipment, and to hire a forester to organise and oversee management plans. |
Technical knowledge | While it is common for community members have a thorough understanding of forest ecology in a natural and historical sense, they often lack the technical knowledge and legal certification required to manage forest resources legally. |
Regulatory obstacles | The forest sector generally has been over-regulated, not under-regulated. In contrast other sectors are generally less regulated and more profitable (e.g. agriculture, mining, tourism, real estate), and conversion is often a less complex and more financially rewarding option than sustainable forest management. An example of this is the forest management plans (FMPs), which tend to be the principal instruments for regulatory compliance. Typically, FMPs have been (and remain) complex, costly, and difficult to develop, implement, monitor, and enforce. [26] In addition, as they rarely consider traditional or local knowledge in promoting sustainability, they make it even more difficult for forest communities to appropriate them or participate in their execution. [27] |
Legal management | Community forestry needs to be based on a legal management plan, prepared and approved by the relevant government authority (usually state environment agencies). Approval of the management plan can often be a long, bureaucratic process. |
Clandestine loggers | Clandestine (illegal) loggers can enter a region and illegally log valuable species without the community's consent, and without a legal management plan. Illegal harvesting often significantly degrades the forest as few limitations are observed by the illegal loggers. Communities are either robbed of their valuable timber, or are paid below market prices. |
Market access | Small villages that are often the focus of community forestry initiatives generally have limited access to markets due to their physical isolation, precarious transport and communication, limited contact with buyers and lack of marketing knowledge. Often they will also face difficulties competing with large-scale operations and illegal timber that flood the market with cheaper products. |
Infrastructure | Forest management, for all types of enterprise, requires a certain amount of physical infrastructure, such as roads, logging equipment, buildings for storage and management headquarters and/or a reliable power supply. |
Managerial skills | Skills related to effective management of the program, business knowhow and entrepreneurial ability, day-to-day decision-making, marketing skills, ability to resolve internal conflicts, and ensuring community benefit sharing are often lacked in rural villages. |
Economic returns | The result of inadequacies in management is small and often insufficient economic returns to keep the program afloat, and furthermore to keep the community interested in the activity. |
Villagers from three communities in Bantaeng district in Indonesia, with the assistance of a funded project obtained a Forest management license and secured a 35-year lease on their local forest. With the incentive to preserve their source of income, the villagers have had a positive impact on forest conservation. This is now viewed as a reference model for the Ministry of Forestry's future projects. [16]
Farmers enter into a profit sharing contract with the 'Village Forestry Association' (VFA) to form a cooperative which assists farmers with reforestation in keeping with the legislation. VFA, though loosely linked to the Office of Forestry enjoys a degree of autonomy facilitating community participation. This system demonstrates the desirable mix of top-down and bottom-up planning ensuring government control as well as effective reforestation through active community participation. [22]
Mexico’s CFEs represent one of the most successful models of community forestry, blending sustainable resource management with economic development. These enterprises emphasize local governance, sustainable practices, and reinvestment in community development. By granting communities legal ownership and management rights, the program has enabled local populations to derive economic benefits from timber and non-timber forest products while conserving biodiversity. These enterprises reinvest profits into community development, creating a cycle of sustainability. [10] [25]
Mozambique’s carbon forestry projects highlight the potential of community forestry to address climate change while generating socio-economic benefits. Communities manage reforested areas, earning carbon credits that can be traded on international markets. However, challenges such as inequitable benefit-sharing and limited technical expertise underscore the need for better governance and capacity-building. [12] [13]
Common land in Nepal is owned by the state while community-based 'Forest User Groups' (FUG) manage forest resources. These groups, composed of local households, are responsible for managing designated forest areas, ensuring sustainable resource use, and distributing benefits equitably. Nepal’s programs demonstrate that community forestry can simultaneously meet ecological and socio-economic goals through decentralized management. For example, the initiative has led to significant forest regeneration, increased household incomes, and strengthened social cohesion, setting a benchmark for community forestry globally. [28] [7]
In the Philippines, NGO-facilitated community forestry projects combine agroforestry with ecotourism to restore degraded landscapes and provide economic opportunities. By diversifying income sources, these projects enhance community resilience and foster long-term sustainability. [17]
Reforestation is the practice of restoring previously existing forests and woodlands that have been destroyed or damaged. The prior forest destruction might have happened through deforestation, clearcutting or wildfires. Three important purposes of reforestation programs are for harvesting of wood, for climate change mitigation, and for ecosystem and habitat restoration purposes. One method of reforestation is to establish tree plantations, also called plantation forests. They cover about 131 million ha worldwide, which is 3% of the global forest area and 45% of the total area of planted forests.
Community-based economics or community economics is an economic system that encourages local substitution. It is similar to the lifeways of those practicing voluntary simplicity, including traditional Mennonite, Amish, and modern eco-village communities. It is also a subject in urban economics, related to moral purchasing and local purchasing.
Illegal logging is the harvest, transportation, purchase, or sale of timber in violation of laws. The harvesting procedure itself may be illegal, including using corrupt means to gain access to forests; extraction without permission, or from a protected area; the cutting down of protected species; or the extraction of timber in excess of agreed limits. Illegal logging is a driving force for a number of environmental issues such as deforestation, soil erosion and biodiversity loss which can drive larger-scale environmental crises such as climate change and other forms of environmental degradation.
The Korea Forest Service is a central administrative agency under the Ministry of Agriculture, Food and Rural Affairs (MAFR), responsible for protecting and nurturing forests, increasing forest resources, developing forest products, conducting research on forest management and improvement, and is located in Daejeon Government Complex. In the past, during the national forestation campaign from 1973 to 1986, it was temporarily under the Ministry of Home Affairs, but returned to the Ministry of Agriculture, Forestry and Fisheries in 1987. However, as the agency's work was focused solely on maintaining and managing successful national forestation policies, questions were raised about its necessity for a period of time. Currently, the agency has transformed its identity into one that strives to generate continuous income through forest resources.
Forest management is a branch of forestry concerned with overall administrative, legal, economic, and social aspects, as well as scientific and technical aspects, such as silviculture, forest protection, and forest regulation. This includes management for timber, aesthetics, recreation, urban values, water, wildlife, inland and nearshore fisheries, wood products, plant genetic resources, and other forest resource values. Management objectives can be for conservation, utilisation, or a mixture of the two. Techniques include timber extraction, planting and replanting of different species, building and maintenance of roads and pathways through forests, and preventing fire.
Natural resource management (NRM) is the management of natural resources such as land, water, soil, plants and animals, with a particular focus on how management affects the quality of life for both present and future generations (stewardship).
Deforestation in Cambodia has increased in recent years. Cambodia is one of the world's most forest endowed countries, that was not historically widely deforested. However, massive deforestation for economic development threatens its forests and ecosystems. As of 2015, the country has one of the highest rates of deforestation in the world.
Ecosystem management is an approach to natural resource management that aims to ensure the long-term sustainability and persistence of an ecosystem's function and services while meeting socioeconomic, political, and cultural needs. Although indigenous communities have employed sustainable ecosystem management approaches implicitly for millennia, ecosystem management emerged explicitly as a formal concept in the 1990s from a growing appreciation of the complexity of ecosystems and of humans' reliance and influence on natural systems.
Community-based management (CBM) is a bottom up approach of organization which can be facilitated by an upper government or NGO structure but it aims for local stakeholder participation in the planning, research, development, management and policy making for a community as a whole. The decentralization of managing tactics enables local people to deal with the unique social, political and ecological problems their community might face and find solutions ideal to their situation. Overwhelming national or local economic, political and social pressures can affect the efficiency of CBM as well as its long term application. CBM varies across spatial and temporal scales to reflect the ever-changing distinctive physical and/or human environment it is acting within. While the specifics of each practice might differ, existing research maintains that community based management, when implemented properly, is incredibly beneficial not only for the health of the environment, but also for the well-being of the stakeholders.
Akure Forest Reserve is a protected area in southwest Nigeria, covering 66 km2 (25 sq mi). The Akure Forest Reserve, established in 1948 and spanning approximately 32 hectares. It was created with the primary aim of safeguarding the genetic diversity of the forest ecosystem. About 11.73% (8.2 km2) is estimated to be cleared for cocoa farming and other food crops. Aponmu and Owena Yoruba speaking communities owned the forest, though, there are also minor settlements surrounding the forest. They include Ipogun, Kajola/ Aponmu, Kajola, Ago Petesi, Akika Camp, Owena Town, Ibutitan/Ilaro Camp, Elemo Igbara Oke Camp and Owena Water new Dam.
Oluwa Forest Reserve is located in Ondo State, Nigeria and covers over 829 km2 (320 sq mi). It is part of the Omo, Shasha and Oluwa forest reserves, although it has become separated from the Omo and Shasha reserves. The three reserves contain some of the last remaining forest in the area. Although they are biologically unique, they are threatened by logging, hunting and agriculture. The natural vegetation of the area is tropical rainforest. However, the natural vegetation of the area except for the areas devoted to forest reserve has now been reduced to secondary regrowth forest and fallow regrowth at varying stages of development or replaced by perennial and annual crops.
Community-based forest management (CBFM) constitutes “a powerful paradigm that evolved out of the failure of state forest governance to ensure the sustainability of forest resources and the equitable distribution of access to and benefits from them”. In 1995, the Philippine government adopted CBFM as a national scheme to promote sustainable forest governance, in recognition of the negative impacts occurring as a result of widespread forest loss across the country. The scheme stresses the importance of involving communities in sustaining the forest through projects such as timber harvesting, agro-forestry and livestock raising. CBFM therefore advocates an increasingly ‘bottom up’ – as opposed to the historically ‘top down’ and centralised - approach to sustainable forest governance involving a variety of stakeholders. By 2005, 5503 projects had been established across the country. For this reason the Philippines has been considered a pioneer within Asia for the successful implementation of CBFM as a nationwide tool of forest governance.
Forest restoration is defined as "actions to re-instate ecological processes, which accelerate recovery of forest structure, ecological functioning and biodiversity levels towards those typical of climax forest", i.e. the end-stage of natural forest succession. Climax forests are relatively stable ecosystems that have developed the maximum biomass, structural complexity and species diversity that are possible within the limits imposed by climate and soil and without continued disturbance from humans. Climax forest is therefore the target ecosystem, which defines the ultimate aim of forest restoration. Since climate is a major factor that determines climax forest composition, global climate change may result in changing restoration aims. Additionally, the potential impacts of climate change on restoration goals must be taken into account, as changes in temperature and precipitation patterns may alter the composition and distribution of climax forests.
Futuro Forestal S.A. is a German-Panamanian reforestation company that operates in Latin America. Established in 1994 in Panama, it is headquartered in Panama City. Futuro Forestal focuses on impact investment management in the tropical forestry industry. To date, the company has planted over 8,000 hectares of teak and mixed hardwood plantations on deforested pastureland, often under the Forest Stewardship Council (FSC) standard.
Centre for People's Forestry is a civil society organisation in India, established in August 2002. CPF works for the rights and livelihoods of forest-dependent communities with due regard to conservation. It believes that the claim to conservation, control and management of the forest resources belong to the forest-dwelling and dependent communities and their livelihoods should be the primary concern of all forestry programmes.
The community forestry program in Nepal is a government effort to reduce forest degradation and to promote sustainable forestry practices as well as to improve the livelihood of the community. It incorporates distinct policies, institutions and practices. The two main goals of the community forestry program is to empower local communities whilst encouraging environmental conservation benefits on the Himalayan forests.
Community Based Mangrove Management (CBMM) is a sustainable approach for conserving the rapidly disappearing mangrove forests. It can be defined as community driven management and rehabilitation of mangrove forests involving resource users in the management process directly. CBMM decentralizes authority and power from government to local communities. The dual aim of CBMM is the ongoing conservation of mangroves and generation of sustainable livelihood.
Ecosystem-based adaptation encompasses a broad set of approaches to adapt to climate change. They all involve the management of ecosystems and their services to reduce the vulnerability of human communities to the impacts of climate change. The Convention on Biological Diversity (CBD) defines EBA as "the use of biodiversity and ecosystem services as part of an overall adaptation strategy to help people to adapt to the adverse effects of climate change".
The biogeographic regionalization of Earth's terrestrial biodiversity, known as Terrestrial Ecoregions of the World (TEOW), is made up of 867 ecoregions that are divided into 14 biomes. In addition to offering a comprehensive map of terrestrial biodiversity, TEOW also provides a global species database for ecological analyses and priority setting, a logical biogeographic framework for large-scale conservation strategies, a map for enhancing biogeographic literacy, and a foundation for the Global 200.
Reforestation in Nigeria employs both natural and artificial methods. Reforestation involves the deliberate planting of trees and restoring forested areas that have been depleted or destroyed. It involves a planned restocking of the forest to ensure sustainable supply of timber and other forest products. Reforestation, in essence, involves replenishing forests to guarantee a consistent and sustainable supply of timber and various other forest resources. This objective can be accomplished through either natural regeneration techniques or artificial regeneration methods. Both of these approaches have been utilized in the reforestation efforts within Nigeria's forests. At the initiation of the reforestation program in Nigeria, the natural regeneration approach was chosen for two primary reasons. Firstly, it aimed to preserve the rainforest in its original state by allowing it to regenerate naturally from the existing seed bank in the soil. Secondly, and of significant importance, this method was selected due to budgetary constraints, as there were insufficient funds available to establish plantations through direct means.
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