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− | [[GIZ HERA Cooking Energy Compendium|--> Back to Overview GIZ HERA Cooking Energy Compendium]]
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− | = Sources of Woodfuel = | + | [[File:GIZ HERA Cooking Energy Compendium small.png|left|831px|GIZ HERA Cooking Energy Compendium|alt=GIZ HERA Cooking Energy Compendium small.png|link=GIZ HERA Cooking Energy Compendium]]<br/><br/><!-- |
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− | Woodfuel originates from a wide range of land-use systems. These including agricultural plantations, agroforestry, trees outside forest, tree plantation, secondary forest management, and primary forest management (see table below). The manner in which wood for energy use is produced of course depends on climatic conditions, vegetation cover, local demand, and infrastructure. But it also depends crucially on land ownership (either prviate, communal, state) and land-use rights (including self management, free access, lease, and transfer of user rights) See the figure below for an illustrational overiew.
| + | -->{{#ifeq: {{#show: {{PAGENAME}} |?Hera category}} | Cooking Energy System |'''[[GIZ HERA Cooking Energy Compendium#Cooking Energy Technologies and Practices|Cooking Energy System]]''' {{!}} | [[GIZ HERA Cooking Energy Compendium#Cooking Energy Technologies and Practices|Cooking Energy System]] {{!}} | }} <!-- |
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| + | -->{{#ifeq: {{#show: {{PAGENAME}} |?Hera category}} | Basics |'''[[GIZ HERA Cooking Energy Compendium#Basics about Cooking Energy|Basics]]''' {{!}} | [[GIZ HERA Cooking Energy Compendium#Basics about Cooking Energy|Basics]] {{!}} | }} <!-- |
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| + | -->{{#ifeq: {{#show: {{PAGENAME}} |?Hera category}} | Policy Advice |'''[[GIZ HERA Cooking Energy Compendium#Policy Advice on Cooking Energy|Policy Advice]]''' {{!}} | [[GIZ HERA Cooking Energy Compendium#Policy Advice on Cooking Energy|Policy Advice]] {{!}} | }} <!-- |
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− | [[File:Origin of Woodfuels.png|742x462px|Origin of Woodfuels.png]] | + | -->{{#ifeq: {{#show: {{PAGENAME}} |?Hera category}} | Planning |'''[[GIZ HERA Cooking Energy Compendium#Planning Cooking Energy Interventions|Planning]]''' {{!}} | [[GIZ HERA Cooking Energy Compendium#Planning Cooking Energy Interventions|Planning]] {{!}} | }} <!-- |
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− | Figure: Origins of woodfuel<ref>S. Sylla (GIZ HERA), S. Sepp (Eco Consult)</ref>
| + | -->{{#ifeq: {{#show: {{PAGENAME}} |?Hera category}} | ICS Supply |'''[[GIZ HERA Cooking Energy Compendium#Designing and Implementing Improved Cookstoves .28ICS.29 Supply Interventions|Designing and Implementing ICS Supply]]''' {{!}} | [[GIZ HERA Cooking Energy Compendium#Designing and Implementing Improved Cookstoves .28ICS.29 Supply Interventions|Designing and Implementing ICS Supply]] {{!}} | }} <!-- |
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| + | -->{{#ifeq: {{#show: {{PAGENAME}} |?Hera category}} | Woodfuel Supply |'''[[GIZ HERA Cooking Energy Compendium#Designing and Implementing Woodfuel Supply Interventions|Designing and Implementing Woodfuel Supply]]''' {{!}} | [[GIZ HERA Cooking Energy Compendium#Designing and Implementing Woodfuel Supply Interventions|Designing and Implementing Woodfuel Supply]] {{!}} | }} <!-- |
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| + | -->{{#ifeq: {{#show: {{PAGENAME}} |?Hera category}} | Climate Change |'''[[GIZ HERA Cooking Energy Compendium#Climate Change Related Issues|Climate Change]]''' | [[GIZ HERA Cooking Energy Compendium#Climate Change Related Issues|Climate Change]] {{!}} | }} <!-- |
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| + | -->{{#ifeq: {{#show: {{PAGENAME}} |?Hera category}} | Extra |'''[[GIZ HERA Cooking Energy Compendium#Climate Change Related Issues|Extra]]''' | [[GIZ HERA Cooking Energy Compendium#Climate Change Related Issues|Extra]] }} |
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| + | = Sources of Woodfuel = |
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− | = <span>Forest </span><span>Energy Plantations</span><br/> =
| + | Woodfuel originates from a wide range of land-use systems. These including agricultural plantations, agroforestry, trees outside forest, tree plantation, secondary forest management, and primary forest management (see table below). The manner in which wood for energy use is produced of course depends on climatic conditions, vegetation cover, local demand, and infrastructure. But it also depends crucially on land ownership (either prviate, communal, state) and land-use rights (including self management, free access, lease, and transfer of user rights) See the figure below for an illustrational overiew. |
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− | <font size="2">Planted forests, established through afforestation or reforestation, have a particularly important role to play in providing a renewable and environmentally friendly energy resource. </font> | + | [[File:Origin of Woodfuels.png|border|left|600px|Origin of Woodfuels.png|alt=Origin of Woodfuels.png]] |
| + | <div style="clear:both"></div> |
| + | Figure: Origins of woodfuel<ref name="S. Sylla (GIZ HERA), S. Sepp (Eco Consult)">S. Sylla (GIZ HERA), S. Sepp (Eco Consult)</ref> |
| + | <p style="text-align: center"><br/></p> |
| + | = Forest Energy Plantations = |
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− | <font size="2"><u>They can play a positive role in:</u></font>
| + | Planted forests, established through afforestation or reforestation, have a particularly important role to play in providing a renewable and environmentally friendly energy resource. |
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− | *<font size="2">Providing ecosystem services, such as preventing erosion, protecting soil and water, and storing carbon etc.</font>
| + | <u>They can play a positive role in:</u> |
− | *<font size="2">Reducing pressure on natural forests</font>
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− | *<font size="2">Restoring marginal or degraded land</font>
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− | *<font size="2">Providing rural employment and development.</font>
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| + | *Providing ecosystem services, such as preventing erosion, protecting soil and water, and storing carbon etc. |
| + | *Reducing pressure on natural forests |
| + | *Restoring marginal or degraded land |
| + | *Providing rural employment and development |
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| + | <br/> |
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− | <font size="2">Currently, there are about 109 million hectares of productive forest plantations in the world. For more information see FAO (2006) [http://www.fao.org/docrep/008/a0400e/a0400e00.htm "Global Forest Resource Assessment 2005"].</font><font size="2"> </font>
| + | Currently, there are about 109 million hectares of productive forest plantations in the world. For more information see FAO (2006) [http://www.fao.org/docrep/008/a0400e/a0400e00.htm "Global Forest Resource Assessment 2005"]. |
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− | <font size="2">In the past, energy plantations were often ill-designed and suffered from insufficient health, vitality, productivity and lacked return on investment. In addition, they were often subject to social and land use conflicts. Many of the plantations failed due to poor management, lack of know-how, and the low commitment of staff in the public forestry services.</font>
| + | In the past, energy plantations were often ill-designed and suffered from insufficient health, vitality, productivity and lacked return on investment. In addition, they were often subject to social and land use conflicts. Many of the plantations failed due to poor management, lack of know-how, and the low commitment of staff in the public forestry services. |
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| Furthermore, there is much controversy about the topic of introduced species versus native specis. It is clear that plantations can be detrimental to biodiversity especially when they are established at the expense of original indigenous forest habitats. Native species should always be given priority. However, the failure of many native species in planting trials regarding growth, resistance to pests, etc, is one of the reasons hindering the wider use of native trees in land rehabilitation. This is often linked to the fact that information on the phenology and silvicultural techniques is lacking, making large scale production in many cases more difficult than with exotics. | | Furthermore, there is much controversy about the topic of introduced species versus native specis. It is clear that plantations can be detrimental to biodiversity especially when they are established at the expense of original indigenous forest habitats. Native species should always be given priority. However, the failure of many native species in planting trials regarding growth, resistance to pests, etc, is one of the reasons hindering the wider use of native trees in land rehabilitation. This is often linked to the fact that information on the phenology and silvicultural techniques is lacking, making large scale production in many cases more difficult than with exotics. |
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− | <font size="2">With increasing pressure on natural forests, alternative sustainable approaches are needed to keep pace with the growing demand for woodfuel. Rising oil prices keep people from climbing the energy ladder, thus increasing their dependence on woodfuel. Consequently, forest plantations need careful development policies, with public sector dominance giving way to more private sector participation, and integrating with other sectors and approaches to provide a sufficient supply of woodfuel.</font>
| + | With increasing pressure on natural forests, alternative sustainable approaches are needed to keep pace with the growing demand for woodfuel. Rising oil prices keep people from climbing the energy ladder, thus increasing their dependence on woodfuel. Consequently, forest plantations need careful development policies, with public sector dominance giving way to more private sector participation, and integrating with other sectors and approaches to provide a sufficient supply of woodfuel. |
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− | <font size="2">The '''Food and Agriculture Organization of the United Nations (FAO)''' has coordinated a multi-stakeholder process between 2004 and 2007 to balance the social, cultural, environmental and economic dimensions of planted forest management and to support their contribution towards sustainable livelihoods and land use through voluntary guidelines for planted forests. These guidelines are tailored primarily to governments, public- and private-sector investors, policymakers and planners. See link below. </font> | + | <br/> |
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− | <font size="2">-> Responsible Management of Planted Forests: [http://www.fao.org/docrep/009/j9256e/J9256E00.htm Voluntary Guidelines]</font><span></span>
| + | The '''Food and Agriculture Organization of the United Nations (FAO)''' has coordinated a multi-stakeholder process between 2004 and 2007 to balance the social, cultural, environmental and economic dimensions of planted forest management and to support their contribution towards sustainable livelihoods and land use through voluntary guidelines for planted forests. These guidelines are tailored primarily to governments, public- and private-sector investors, policymakers and planners. See link below. |
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− | <font size="2">Generally, the establishment of plantations on pristine or almost pristine forest lands is not recommended. </font> <font size="2">Hardwood species generally have the greatest potential for woodfuel. The type selected should coppice readily, be a variety that fixes nitrogen, and be a multi-purpose species (meaning a species which can serve several purposes, such as providing fruits, habitat, shade, or soil improvement). Selection also depends on what can be grown easily on the site and what is acceptable to the users. Cultivation methods should be adapted to the skills and resources of the rural people. Care in the establishment phase is very important. Every plantation activity should be preceded by an economic analysis. Sustainability can only be assured when the returns on investment are significant for the plantation owner and have a positive social and ecological potential.</font>
| + | -> Responsible Management of Planted Forests: [http://www.fao.org/docrep/009/j9256e/J9256E00.htm Voluntary Guidelines] |
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− | <font size="2">-> The following excel-based program (in French) allows users to quickly determine the economic viability of woodfuel plantation programmes:</font> [http://energypedia.info/index.php/file:Analysefinanciere_2007_02_26.xls Guide de l'utilisateur du modèle "Analyse Financière"] | + | <br/> |
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− | <font size="2">In Madagascar, GIZ adopted a village-based approach of making local people the centre of planning and implementation of woodfuel plantations. Individuals are given the property rights of degraded community land for reforestation. The project provides institutional and technical support, and the soil is initially prepared by tractor before handover. The plantation owner is responsible for raising seedlings and maintaining the plantation. An overall GIS based monitoring system gives data on each and every plantation plot, including productivity figures, income generated, etc. To date (2011), more than 6500 hectares have been planted in Madagascar, providing an increase in income of more than 20% for more than 2000 rural households.</font>
| + | Generally, the establishment of plantations on pristine or almost pristine forest lands is not recommended. Hardwood species generally have the greatest potential for woodfuel. The type selected should coppice readily, be a variety that fixes nitrogen, and be a multi-purpose species (meaning a species which can serve several purposes, such as providing fruits, habitat, shade, or soil improvement). Selection also depends on what can be grown easily on the site and what is acceptable to the users. Cultivation methods should be adapted to the skills and resources of the rural people. Care in the establishment phase is very important. Every plantation activity should be preceded by an economic analysis. Sustainability can only be assured when the returns on investment are significant for the plantation owner and have a positive social and ecological potential. |
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− | <font size="2">-> The approach is described in the brochure:</font> [https://energypedia.info/images/thumb/2/28/Le_reboisement_individuel_villageois-small.pdf/page1-154px-Le_reboisement_individuel_villageois-small.pdf.jpg <span><font size="2">L</font></span><span><font size="2">e</font></span><span><font size="2">Reboisement <font size="2">villageois</font> individuel.</font></span><span></span>]
| + | -> The following excel-based program (in French) allows users to quickly determine the economic viability of woodfuel plantation programmes:[[:file:Analysefinanciere 2007 02 26.xls|Guide de l'utilisateur du modèle "Analyse Financière"]] |
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− | <br/>Also noteworthy is an approach known as “'''rainforestation farming'''” in which native or local trees are used to rehabilitate degraded landscapes and restore key ecosystem services and functions, while providing forest-dependent communities with an alternative source of livelihood. This system was developed in the 1990s with support of GIZ and in collaboration with the Visayas State University in the Philippines and is currently being increasingly propagated throughout the country and beyond. | + | <br/> |
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− | -> Further information can be obtained at the following internet site: [http://www.rainforestation.ph/index.html Rainforestation:Return of the Natives] | + | In Madagascar, GIZ adopted a village-based approach of making local people the centre of planning and implementation of woodfuel plantations. Individuals are given the property rights of degraded community land for reforestation. The project provides institutional and technical support, and the soil is initially prepared by tractor before handover. The plantation owner is responsible for raising seedlings and maintaining the plantation. An overall GIS based monitoring system gives data on each and every plantation plot, including productivity figures, income generated, etc. To date (2011), more than 6500 hectares have been planted in Madagascar, providing an increase in income of more than 20% for more than 2000 rural households. |
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− | <font size="2">Another type of scheme known as the ‘'''outgrower scheme'''’ is a relatively new development in the African forestry sector. It entails companies entering into long-term partnerships with small growers. The companies provide financing (loans) and inputs such as seedlings and extension support for the establishment and maintenance of the woodlots. For the companies, these schemes <span>address the need to develop long-term timber/woodfuel supplies without tying up large amounts of capital in land holdings when all they require is wood. The outgrower scheme is described in more detail in the following FAO report from 2001:</span></font>
| + | -> The approach is described in the brochure:[[:File:Le reboisement individuel villageois-small.pdf|Le reboisement villageois individuel]] |
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− | <font size="2">''-> ''Forestry Out-Grower Schemes: [http://www.fao.org/docrep/004/AC131E/ac131e00.htm A Global View]</font><span style="color: rgb(0,0,255)"></span> | + | <br/>Also noteworthy is an approach known as “'''rainforestation farming'''” in which native or local trees are used to rehabilitate degraded landscapes and restore key ecosystem services and functions, while providing forest-dependent communities with an alternative source of livelihood. This system was developed in the 1990s with support of GIZ and in collaboration with the Visayas State University in the Philippines and is currently being increasingly propagated throughout the country and beyond. |
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| + | -> Further information can be obtained at the following internet site: [http://www.rainforestation.ph/index.html Rainforestation:Return of the Natives] |
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| + | <br/> |
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− | = Management of Natural Forests<br/> =
| + | Another type of scheme known as the ‘'''outgrower scheme'''’ is a relatively new development in the African forestry sector. It entails companies entering into long-term partnerships with small growers. The companies provide financing (loans) and inputs such as seedlings and extension support for the establishment and maintenance of the woodlots. For the companies, these schemes address the need to develop long-term timber/woodfuel supplies without tying up large amounts of capital in land holdings when all they require is wood. The outgrower scheme is described in more detail in the following FAO report from 2001: |
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− | <font size="2">Management of natural forests is a very complex undertaking in areas where the supply of woodfuel is usually a by-product of more valuable products such as timber, poles etc.</font>
| + | ''-> ''Forestry Out-Grower Schemes: [http://www.fao.org/docrep/004/AC131E/ac131e00.htm A Global View] |
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− | <font size="2">Woodfuel shortages generally occur in regions where savannah-type vegetation is predominant due to low and erratic rainfall patterns. These savannah woodlands are not well suited for high-value timber production, although they may make a major contribution to non-timber forest products such as fodder, gums, resins, etc.</font>
| + | [[Woodfuel Production Options#toc|►Go to Top]] |
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− | <font size="2">The sustainable management of using these savannah woodlands for fuel is often described as '''Participatory Forest Management (PFM)''' or Community based forest (natural resources) management. </font>
| + | = Management of Natural Forests<br/> = |
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− | <font size="2">PFM experienced a particular impetus due to increasing decentralization efforts, in which </font><font size="2">management responsibility over state-owned forests is increasingly being transfered to local communities. In order to implement a PFM approach and to get local people to invest in sustainable forest management, issues around land tenure and the secure transfer of decision-making powers from central government to local institutions have to be resolved</font><font size="2">.</font>
| + | Management of natural forests is a very complex undertaking in areas where the supply of woodfuel is usually a by-product of more valuable products such as timber, poles etc. |
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− | <font size="2">-> Recommendations and potential pitfalls around decentralization of natural resources management are described in a publication of the ‘The World Resources Institute’ [http://pdf.wri.org/ddnr_full_revised.pdf <span style="line-height: 115%">Democratic Decentralization of Natural Resources</span>]<span style="line-height: 115%"></span></font>
| + | Woodfuel shortages generally occur in regions where savannah-type vegetation is predominant due to low and erratic rainfall patterns. These savannah woodlands are not well suited for high-value timber production, although they may make a major contribution to non-timber forest products such as fodder, gums, resins, etc. |
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| + | The sustainable management of using these savannah woodlands for fuel is often described as '''Participatory Forest Management (PFM)''' or Community based forest (natural resources) management. |
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| + | PFM experienced a particular impetus due to increasing decentralization efforts, in which management responsibility over state-owned forests is increasingly being transfered to local communities. In order to implement a PFM approach and to get local people to invest in sustainable forest management, issues around land tenure and the secure transfer of decision-making powers from central government to local institutions have to be resolved. |
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| + | -> Recommendations and potential pitfalls around decentralization of natural resources management are described in a publication of the ‘The World Resources Institute’ [http://www.wri.org/publication/democratic-decentralization-natural-resources Democratic Decentralization of Natural Resources] |
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− | {| border="1" cellpadding="1" cellspacing="1" width="100%" | + | {| style="width: 100%" cellspacing="1" cellpadding="1" border="1" |
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| '''Manuals on Participatory Forest Management''' | | '''Manuals on Participatory Forest Management''' |
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− | <span style="font-size: 9pt; line-height: 115%">-> The CILSS-based project PREDAS published a [http://www.cilss.bf/predas/publications/Guide%20amenagement%20forestier%20villageois.pdf manual on community based forest management for woodfuel production for energy].</span>
| + | -> The CILSS-based project PREDAS published a [http://secheresse.info/spip.php?article12093 amenagement forestier villageois.pdf amenagement forestier villageois.pdf amenagement forestier villageois.pdf manual on community based forest management for woodfuel production for energy]. |
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− | <span style="font-size: 9pt; line-height: 115%">-> A [http://www.farmafrica.org.uk/resources/Key%20Steps%20in%20Establishing%20Participatory%20Forest%20Management.pdf field manual explaining the key steps of establishing Participatory Forest Management in Ethiopia] has been put together as the result of ten years’ practical experience by FARM-Africa and SOS Sahel Ethiopia.</span>
| + | -> A [http://www.eap.gov.et/?q=node/604 Steps in Establishing Participatory Forest Management.pdf field manual explaining the key steps of establishing Participatory Forest Management in Ethiopia] has been put together as the result of ten years’ practical experience by FARM-Africa and SOS Sahel Ethiopia. |
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− | <span style="font-size: 9pt; line-height: 115%">-> UNHCR published a [http://data.iucn.org/dbtw-wpd/edocs/2005-034.pdf guide on forest management practices to react on some degree of forest degradation and deforestation in the refugee and returnee context].</span>
| + | -> UNHCR published a [http://data.iucn.org/dbtw-wpd/edocs/2005-034.pdf guide on forest management practices to react on some degree of forest degradation and deforestation in the refugee and returnee context]. |
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| + | The following features were found to be particularly important when designing and implementing PFM projects for energy supply: |
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| + | *PFM activities should take place after stakeholder consultations to enhance awareness of the causes and consequences of uncontrolled exploitation and the benefits of available techniques for forest rehabilitation. |
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| + | -> Example of an animation tutorial for awareness campaigns: des villages verts. [[:File:Guide de l animteur dgis.doc|Guide de l'animateur]] |
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− | <u><font size="2">The following features were found to be particularly important when designing and implementing PFM projects for energy supply:</font></u> | + | <br/> |
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− | *<span style="font-size: 10pt; line-height: 115%">PFM activities should take place after stakeholder consultations to enhance awareness of the causes and consequences of uncontrolled exploitation and the benefits of available techniques for forest rehabilitation.</span> | + | *Baseline studies are fundamental tools for assessing success or failure of intended PFM activities. |
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− | <span style="font-size: 10pt; line-height: 115%"> -> Example of an animation tutorial for awareness campaigns: des villages verts. [http://energypedia.info/index.php/File:Guide_d_%27animation.pdf Guide de l'animateur]</span>
| + | -> Example of different tools and techniques to facilitate collection and analysis of information: [http://www.asiaforestnetwork.org/pub/pub20.pdf PARTICIPATORY RURAL APPRAISAL FOR COMMUNITY FOREST MANAGEMENT] |
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− | *<span style="font-size: 10pt; line-height: 115%">Baseline studies are fundamental tools for assessing success or failure of intended PFM activities.</span>
| + | <br/> |
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− | <span style="font-size: 10pt; line-height: 115%"> -> Example of different tools and techniques to facilitate collection and analysis of information:</span>
| + | *Distribution of power and responsibility by the government services (forest department) to the community requires critical analysis and informed public debate. It depends on the ownership of forest land (public, community or private). Equitable sharing of costs and benefits within the communities and between the communities and the government have to be clearly defined. The results should be recorded as an agreement, providing the basis for PFM activities. |
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− | <span style="font-size: 10pt; line-height: 115%"> </span>[http://www.communityforestryinternational.org/publications/field_methods_manual/pra_manual_tools_and_techniques.pdf PARTICIPATORY RURALAPPRAISAL FOR COMMUNITY FOREST MANAGEMENT]
| + | -> Example of a local agreement: [[:File:Peracod-conventions locales.pdf|Les conventions locales]][[:File:Peracod-conventions locales.pdf|Un outil fonctionnel dans la gestion forestière decentralisée]] |
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− | *<span style="font-size: 10pt; line-height: 115%">Distribution of power and responsibility by the government services (forest department) to the community requires critical analysis and informed public debate. It depends on the ownership of forest land (public, community or private). Equitable sharing of costs and benefits within the communities and between the communities and the government have to be clearly defined. The results should be recorded as an agreement, providing the basis for PFM activities.</span>
| + | <br/> |
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− | <span style="font-size: 10pt; line-height: 115%"> -> Example of a local agreement: </span>[http://energypedia.info/index.php?title=File:Peracod-conventions_locales.pdf&page=1 <span style="font-size: 10pt; line-height: 115%">Les conventions locales</span>]<span style="font-size: 10pt; line-height: 115%">[http://energypedia.info/index.php?title=File:Peracod-conventions_locales.pdf&page=1 . Un outil fonctionnel dans la gestion forestière decentralisée]</span>
| + | *Functional institutional frameworks at village level to oversee planning, implementation and monitoring have to be established. Such a local management structure should be governed by the Community or Village Assembly. Clear guidelines have to be developed to specify the responsibilities of each and every member within the local management structure. |
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− | *<span style="font-size: 10pt; line-height: 115%">Functional institutional frameworks at village level to oversee planning, implementation and monitoring have to be established. Such a local management structure should be governed by the <font size="2">Community or Village Assembly. Clear guidelines have to be developed to specify the responsibilities of each and every member within the local management structure. </font></span>
| + | -> Example of the institutional framework of a local management structure: [[:File:Manuel de création slg.pdf|Manuel pour la mise en place des structures locales de gestion (SLG)]] |
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− | <span style="font-size: 10pt; line-height: 115%"><font size="2"> -> Example of the institutional framework of a local management structure</font>: </span><span style="font-size: 10pt; line-height: 115%"></span> | + | <br/> |
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− | <span style="font-size: 10pt; line-height: 115%">[http://energypedia.info/index.php/File:Manuel_de_cr%C3%A9ation_slg.pdf Manuel pour la mise en place des structures locales de gestion (SLG)]</span><span style="font-size: 10pt; line-height: 115%"></span>
| + | *Forest management plans must be simple and short and should be developed through participatory action in a way that is accessible for communities where literacy levels are low. To foster local ‘ownership’ of such a management plan, the contents of the plan must include the knowledge, experience and expectations of the local community about their forest. |
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− | *<font size="2">Forest management plans must be simple and short and should be developed through participatory action in a way that is accessible for communities where literacy levels are low. To foster local ‘ownership’ of such a management plan, the contents of the plan must include the knowledge, experience and expectations of the local community about their forest.</font>
| + | -> [http://www.fao.org/docrep/008/j4817e/j4817e00.htm General Guideline to establish simple forest management plans] |
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− | <font size="2"> -> </font>[http://www.fao.org/docrep/008/j4817e/j4817e00.htm <font color="#002bb8" size="2">General Guideline to establish simple forest management plans</font>]
| + | -> Example of a manual for simple management plans for woodfuel production in Chad: [[:File:Instr plan gestion.pdf|Instruction pour l'élaboration des Plans de Gestion Forestière Simplifiés au Niveau des Villages VERTS]] |
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− | -> Example of a manual for simple management plans for woodfuel production in Chad:
| + | <br/> |
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− | [http://energypedia.info/index.php?title=File:Instr_plan_gestion.pdf&page=1 <font color="#002bb8"> Instruction pour l'élaboration des Plans de Gestion Forestière Simplifiés au Niveau des Villages VERTS</font>]
| + | *In open access areas, sustainable forest management competes with uncontrolled exploitation (where the woodfuel price does not reflect any replacement costs). In these situations, communities investing in sustainable forest management tend to lose their motivation and give up because of lack of incentive. The introduction of a differential tax system is essential to provide a fiscal incentive to firewood traders who access their fuel from sustainably managed forests rather than from the uncontrolled exploitation of natural woodlands. An effective control system has to be put in place to enforce the differential tax system or it fails to work and has no impact. |
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− | *In open access areas, sustainable forest management competes with uncontrolled exploitation (where the woodfuel price does not reflect any replacement costs). In these situations, communities investing in sustainable forest management tend to lose their motivation and give up because of lack of incentive. The introduction of a differential tax system is essential to provide a fiscal incentive to firewood traders who access their fuel from sustainably managed forests rather than from the uncontrolled exploitation of natural woodlands. An effective control system has to be put in place to enforce the differential tax system or it fails to work and has no impact.
| + | <br/> |
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| + | A good example of a successfuel PFM for energy is the introduction of '''rural woodfuel markets (RWM)''' in Africa (e.g. Niger, Mali, Madagascar, Senegal). A RWM is a place where woodfuel dealers can buy firewood and charcoal drawn from an area of natural woodland formally delimited and agreed between the villages and the local authorities. This woodland area is managed using a simple plan agreed between the village associations and the local forestry service. It includes: |
| | | |
| + | #an annual woodfuel quota that stays below the annual production rate (safety margin) |
| + | #a set of very simple silvicultural and woodfuel cutting rules. Rural woodfuel markets are run by a local management structure. The CILSS-based EU-supported project PREDAS has published a guide on how to create woodfuel markets. |
| + | <p style="text-align: center">[[File:Guide marches ruraux.pdf|border|center|200px|Guide marches ruraux.pdf|alt=Guide marches ruraux.pdf]]</p><p style="text-align: center">Guide de création des marchés ruraux</p><p style="text-align: center"><br/></p> |
| + | In Ethiopia, a PFM approach called WAJIB has been developed with GIZ support in which a binding agreement is made between the local forest user groups and the district forest office. There are clearly defined rights, duties and obligations for both partners. This approach differs from many other PFM approaches in Africa as the number of participating households is limited by the forest carrying capacity and the economic potential. The underlying assumption is that households will only invest in forestry operations if they can make a living out of sustainable forest management. Thus, the forest in a given village is subdivided into forest blocks with an average size of 360 hectares. Based on the forest carrying capacity of 12 hectares per household, each block is managed by a WAJIB group of not more than 30 households. Each WAJIB group has its own internal regulations (by-laws), which govern the use, protection, rights and responsibilities of each household within the block. The main duty of the forest administration is to provide technical advice to the WAJIB groups on how to develop and utilize the forest on a sustainable basis. |
| | | |
− | <font size="2">A good example of a successfuel PFM for energy is the introduction of '''rural woodfuel markets (RWM)''' in Africa (e.g. Niger, Mali, Madagascar, Senegal). A RWM is a place where woodfuel dealers can buy firewood and charcoal drawn from an area of natural woodland formally delimited and agreed between the villages and the local authorities. This woodland area is managed using a simple plan agreed between the village associations and the local forestry service.</font> <u><font size="2">It includes:</font></u> | + | <br/> |
| | | |
− | #<font size="2">an annual woodfuel quota that stays below the annual production rate (safety margin)</font>
| + | The following documents describe the WAJIB approach: |
− | #<font size="2">a set of very simple silvicultural and woodfuel cutting rules. Rural woodfuel markets are run by a local management structure. The CILSS-based EU-supported project PREDAS has published a guide on how to create woodfuel markets.</font>
| + | |
| | | |
− | [[File:Guide marches ruraux.pdf|198x280px|Guide marches ruraux.pdf]] | + | *[[:File:Guidelines for Implementation of the WAJIB Approach in Ethiopia .pdf|Guidelines of the WAJIB approach]] |
| + | *[[:File:Forest block allocation agreement.pdf|Forestblock allocation agreement]] |
| + | *[[:File:Model bylaw wajib.pdf|Model of a forest by-law]] |
| | | |
− | <font size="2">Guide</font> de création des marchés ruraux | + | <br/> |
| | | |
− | <font size="2">In Ethiopia, a PFM approach called WAJIB has been developed with GIZ support in which a binding agreement is made between the local forest user groups and the district forest office. There are clearly defined rights, duties and obligations for both partners. This approach differs from many other PFM approaches in Africa as the number of participating households is limited by the forest carrying capacity and the economic potential. The underlying assumption is that households will only invest in forestry operations if they can make a living out of sustainable forest management. Thus, the forest in a given village is subdivided into forest blocks with an average size of 360 hectares. Based on the forest carrying capacity of 12 hectares per household, each block is managed by a WAJIB group of not more than 30 households. Each WAJIB group has its own internal regulations (by-laws), which govern the use, protection, rights and responsibilities of each household within the block. The main duty of the forest administration is to provide technical advice to the WAJIB groups on how to develop and utilize the forest on a sustainable basis.</font>
| + | In Southern Africa, the miombo woodlands are the major sources of fuel. Miombo woodlands are tropical and subtropical grasslands, savannas, and shrublands. These woodlands provide a wide range of products (including timber) and services to rural households, so the forest management approaches need to be very diverse and often embedded in an integrated land use approach. The opportunities and barriers to sustainable management of miombo forests are described in the CIFOR publication [http://www.cifor.org/miombo/docs/Campbell_BarriersandOpportunities.pdf Woodlands – Opportunities and Barriers to Sustainable Forest Management 2007].<br/> |
| | | |
− | <u><font size="2">The following documents describe the WAJIB approach:</font></u>
| + | By harvesting woodfuel, people make an impact on the state of their forests. The impact of these activities on the environment is hard to predict. Ecological monitoring is more and more recognized as a helpful method in natural resource management. The following manual, which discusses community-based ecological monitoring, gives advice to the practitioner of how to conduct such an activity: [http://www.landcoalition.org/pdf/07_SAFIRE_Community_based_ecological_monitoring_Manual.pdf Community Based Ecological Monitoring]. |
| | | |
− | *<span style="font-size: 10pt; line-height: 115%">[http://energypedia.info/index.php?title=File:Wajib_guidlines.pdf&page=1 Guidelines of the WAJIB approach]</span>
| + | <br/> |
− | *[http://energypedia.info/index.php?title=File:Forest_block_allocation_agreement.pdf&page=1 <span style="font-size: 10pt; line-height: 115%">Forest</span><span style="font-size: 10pt; line-height: 115%">block allocation agreement</span>]
| + | |
− | *[http://energypedia.info/index.php?title=File:Model_bylaw_wajib.pdf&page=1 <span style="font-size: 10pt; line-height: 115%">Model of a forest by-law</span>]
| + | |
| | | |
| + | [[Woodfuel Production Options#toc|►Go to Top]]<br/> |
| | | |
| + | = Trees Outside Forests (TOFs)<br/> = |
| | | |
− | <font size="2">In Southern Africa, the miombo woodlands </font><font size="2">are the major sources of fuel. Miombo woodlands are tropical and subtropical grasslands, savannas, and shrublands. These woodlands provide a wide range of products (including timber) and services to rural households, so the forest management approaches need to be very diverse and often embedded in an integrated land use approach. The opportunities and barriers to sustainable management of miombo forests are described in the CIFOR publication "[http://forestle.org/goto.php?q=Miombo%20woodlands%20%E2%80%93%20opportunities%20and%20barriers%20%20to%20sustainable%20forest%20management%20%20&url=http%3A%2F%2Fwww.cifor.cgiar.org%2Fmiombo%2Fdocs%2FMiombo2007.pdf Miombo woodlands - opportunities and barriers to sustainable forest management]"</font><font size="2">2007.</font>
| + | '''Trees outside forests (TOFs) '''include all trees found on non-forest and non-wooded lands, such as agricultural lands, in urban and settlement areas, along roads, in home gardens, in hedgerows, scattered in the landscape and on pasture and rangelands. Most knowledge on TOFs comes from experience in agroforestry. Agroforestry is the practice of growing trees and agricultural products on the same piece of ground, and at the same time. <Agroforestry helps farmers create more integrated, diverse, productive, profitable, healthy and sustainable land-use systems. |
| | | |
− | <u><font size="2">For further information on miombo woodlands, consult the miombo network internet site:</font></u>
| + | Although TOFs fulfil a multipurpose function, and are part of an integrated land-use system, woodfuel can be a main product. The FAO (2001) cites references in the Asia-Pacific area, where over two-thirds of the energy demand is supplied by fuelwood from non-forest sources, providing fuel for two billion people. |
| | | |
− | *[http://www.geog.psu.edu/geclab/miombo/index.html <span style="color: rgb(0, 0, 255)"><font size="2">http://www.geog.psu.edu/geclab/miombo/index.html</font></span>]
| + | Trees for fuelwood can be planted dispersed, in a row, on crop land (alley cropping), in home-gardens, as replacement, or by the introduction of selected trees or shrubs to enhance natural fallow vegetation. To control soil and water erosion, trees and shrubs are planted as living barriers along the contour lines of a slope or terrace. Living fences planted as lines of trees on farm boundaries or on pasture plots, animal enclosures or around agricultural fields can contribute to the energy supply of local households. The Agroforestry extension manual for Kenya provides an excellent overview of the different approaches, illustrated by a number of case reports. |
| | | |
| + | ''-> ''[http://www.worldagroforestry.org/Units/Library/Books/PDFs/06_Agroforestry_extension_manual_for_kenya.pdf?n=141 Agroforestry Extension Manual for Kenya](1994) |
| | | |
| + | <br/> |
| | | |
− | <font size="2">By harvesting woodfuel, people make an impact on the state of their forests. The impact of these activities on the environment is hard to predict. Ecological monitoring is more and more recognized as a helpful method in natural resource management. The following manual, which discusses community-based ecological monitoring, gives advice to the practitioner of how to conduct such an activity: [http://www.landcoalition.org/pdf/07_SAFIRE_Community_based_ecological_monitoring_Manual.pdf Community Based Ecological Monitoring]</font><font size="2">.</font>
| + | As with forest energy plantations, hardwood species that coppice readily and fix nitrogen should be selected (see Table 6) . They should be fast growing hardwoods which can be harvested after 4-6 years, well-adapted to the site, easy to grow, and resistant to goats and wildlife damage. The World Agroforestry Centre maintains a freely accessible database providing information on the management, use and ecology of a wide range of tree species that can be used for fuelwood in agroforestry. |
| | | |
| + | [http://www.worldagroforestrycentre.org/our_products/databases -> worldagroforestry.org]<br/> |
| | | |
| + | <br/> |
| | | |
− | = Trees Outside Forests (TOFs)<br/> =
| + | Lack of accessible fuelwood supplies often affects women the hardest. Thus, it is important to integrate their concerns when designing agroforestry projects. The World Agroforestry Centre published a guide on how to integrate gender issues when programming agroforestry initiatives in the Sahel.<br/>''-> ''[http://www.worldagroforestry.org/downloads/publications/PDFS/OP14807.pdf Intégration du genre dans la mise en œuvre d’un programme agroforestier au Sahel : Guide pratique des chercheurs] |
| | | |
− | <font size="2">'''Trees outside forests (TOFs) '''include all trees found on non-forest and non-wooded lands, such as agricultural lands, in urban and settlement areas, along roads, in home gardens, in hedgerows, scattered in the landscape and on pasture and rangelands. Most knowledge on TOFs comes from experience in agroforestry. Agroforestry is the practice of growing trees and agricultural products on the same piece of ground, and at the same time. </font><font size="2">Agroforestry helps farmers create more integrated, diverse, productive, profitable, healthy and sustainable land-use systems.</font> | + | <br/> |
| | | |
− | <font size="2">Although TOFs fulfil a multipurpose function, and are part of an integrated land-use system, woodfuel can be a main product. The FAO (2001) cites references in the Asia-Pacific area, where over two-thirds of the energy demand is supplied by fuelwood from non-forest sources, providing fuel for two billion people.</font>
| + | The Sahel Eco-Farm (SEF) approach to agroforestry has been developed with the support of ICRISAT. It is a good example of an agroforestry-based system combining ecological advantages (such as improving microclimate) and soil conditions, with income generation. This approach improves the livelihoods of the rural poor in vulnerable regions such as the Sahel. The SEF is based on an alley cropping system, in which trees and/or shrubs are intercropped with annual crops.<ref name="The Sahelian Eco-Farm: http://www.worldwidewattle.com/infogallery/utilisation/sehelian-eco-farm.pdf">The Sahelian Eco-Farm: http://www.worldwidewattle.com/infogallery/utilisation/sehelian-eco-farm.pdf</ref> |
| | | |
− | <font size="2">Trees for fuelwood can be planted dispersed, in a row, on crop land (alley cropping), in home-gardens, as replacement, or by the introduction of selected trees or shrubs to enhance natural fallow vegetation. To control soil and water erosion, trees and shrubs are planted as living barriers along the contour lines of a slope or terrace. Living fences planted as lines of trees on farm boundaries or on pasture plots, animal enclosures or around agricultural fields can contribute to the energy supply of local households. The Agroforestry extension manual for Kenya provides an excellent overview of the different approaches, illustrated by a number of case reports.</font> | + | <br/> |
| | | |
− | <font size="2">''-> ''[http://www.worldagroforestry.org/Units/Library/Books/PDFs/06_Agroforestry_extension_manual_for_kenya.pdf?n=141 Agroforestry Extension Manual for Kenya] </font><font size="2">(1994)</font> | + | A good example of increasing fuelwood supply is by planting nitrogen-fixing trees that can be harvested for fuelwood or charcoal after 3-4 years as part of a system to improve fallow fields. In Chapter 6 of a recent publication by the World Agroforestry Centre on innovative agroforestry approaches, an improved fallow system is described. See:<br/>''-> ''[http://www.worldagroforestrycentre.org/downloads/publications/PDFS/b14409.pdf World Agroforestry into the Future] |
| | | |
− | <font size="2">As with forest energy plantations, hardwood species that coppice readily and fix nitrogen should be selected (see Table 6) . They should be fast growing hardwoods which can be harvested after 4-6 years, well-adapted to the site, easy to grow, and resistant to goats and wildlife damage. The World Agroforestry Centre maintains a freely accessible database providing information on the management, use and ecology of a wide range of tree species that can be used for fuelwood in agroforestry. </font> | + | <br/> |
| | | |
− | [http://www.worldagroforestry.org/Sites/TreeDBS/TreeDatabases.asp <span style="color: rgb(0,0,255)"><font size="2">-> http://www.worldagroforestry.org/sea/Products/AFDbases/af/index.asp</font></span>]
| + | Enough wood can be obtained from one hectare of improved fallow to supply the fuelwood needs of a typical 6–7 member rural household for 6–8 months. |
| | | |
− | <font size="2">Lack of accessible fuelwood supplies often affects women the hardest. Thus, it is important to integrate their concerns when designing agroforestry projects. The World Agroforestry Centre published a guide on how to integrate gender issues when programming agroforestry initiatives in the Sahel.<br/>''-> ''[http://www.worldagroforestry.org/downloads/publications/PDFS/OP14807.pdf Intégration du genre dans la mise en œuvre d’un programme agroforestier au Sahel : Guide pratique des chercheurs]</font>
| + | Another key initiative is to promote agroforestry at policy level so that it is recognized as one of the most important fuelwood supply resources, besides natural forests and plantations. The socio-economic and ecological advantages of agroforestry substantially outweigh many expensive, ill-conceived tree plantation programmes. Agroforestry can be developed at a fraction of the cost of large-scale plantations, and the approach encourages greater local participation and a wider diversity of goods and services for the local and national economies. |
| | | |
− | <font size="2">The Sahel Eco-Farm (SEF) approach to agroforestry has been developed with the support of ICRISAT. It is a good example of an agroforestry-based system combining ecological advantages (such as improving microclimate) and soil conditions, with income generation. This approach improves the livelihoods of the rural poor in vulnerable regions such as the Sahel. The SEF is based on an alley cropping system, in which trees and/or shrubs are intercropped with annual crops.<ref>The Sahelian Eco-Farm: http://www.worldwidewattle.com/infogallery/utilisation/sehelian-eco-farm.pdf</ref></font> | + | <br/> |
| | | |
− | <font size="2">A good example of increasing fuelwood supply is by planting nitrogen-fixing trees that can be harvested for fuelwood or charcoal after 3-4 years as part of a system to improve fallow fields. In Chapter 6 of a recent publication by the World Agroforestry Centre on innovative agroforestry approaches, an improved fallow system is described. See:<br/>''-> ''[http://www.worldagroforestrycentre.org/downloads/publications/PDFS/b14409.pdf World Agroforestry into the Future]</font> | + | <u>Further Information is provided by following internet sites:</u> |
| | | |
− | <font size="2">Enough wood can be obtained from one hectare of improved fallow to supply the fuelwood needs of a typical 6–7 member rural household for 6–8 months.</font> | + | *<u>[http://www.fao.org/docrep/005/y2328e/y2328e00.HTM Trees outside forests]</u> |
| | | |
− | <font size="2">Another key initiative is to promote agroforestry at policy level so that it is recognized as one of the most important fuelwood supply resources, besides natural forests and plantations. The socio-economic and ecological advantages of agroforestry substantially outweigh many expensive, ill-conceived tree plantation programmes. Agroforestry can be developed at a fraction of the cost of large-scale plantations, and the approach encourages greater local participation and a wider diversity of goods and services for the local and national economies.</font> | + | <br/> |
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− | | + | {| style="width: 100%" class="FCK__ShowTableBorders" cellspacing="0" cellpadding="0" |
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− | <u><font size="2">Further Information is provided by following internet sites:</font></u>
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− | *[http://www.fao.org/forestry/tof/en/ <font size="2">Trees outside forests</font>]
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− | | style="border-right: rgb(224,223,227); border-top: rgb(224,223,227); border-left: rgb(224,223,227); border-bottom: rgb(224,223,227); background-color: transparent" | <div>[[File:FAO table woodfuel species.jpg|RTENOTITLE]]</div> | + | | style="border: rgb(224, 223, 227); background-color: transparent" | <u>[[File:FAO table woodfuel species.jpg|left|400px|RTENOTITLE]]</u> |
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− | Table 6: Useful woodfuel species for tropical developing countries<ref>Agroforestry: http://www.worldagroforestry.org (based on National Academy of Sciences 1980, 1983, Nair 1993, FAO 2000, FFRD, 1994)</ref> | + | <u>Table 6: Useful woodfuel species for tropical developing countries<ref name="Agroforestry: http://www.worldagroforestry.org (based on National Academy of Sciences 1980, 1983, Nair 1993, FAO 2000, FFRD, 1994)">Agroforestry: http://www.worldagroforestry.org (based on National Academy of Sciences 1980, 1983, Nair 1993, FAO 2000, FFRD, 1994)</ref></u> |
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| + | <br/> |
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− | <div>
| + | [[Woodfuel Production Options#toc|►Go to Top]]<br/> |
− | = Further Information<br/> =
| + | |
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− | {| border="1" cellpadding="1" cellspacing="1" width="100%" | + | = Further Information = |
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| + | {| style="width: 100%" cellspacing="1" cellpadding="1" border="1" |
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− | Further information on wood energy issues can also be found on the recently launched FAO internet site: [http://www.fao.org/forestry/energy/en/ '''http://www.fao.org/forestry/energy/en/'''] | + | Further information on wood energy issues can also be found on the recently launched [http://www.fao.org/forestry/energy/en/ FAO internet site.]<br/> |
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− | | | + | | [[:File:2010 FAO sustainable woodfuel guidelines-1-.pdf|Criteria and indicators for sustainable woodfuels]] |
− | [http://energypedia.info/index.php/File:2010_FAO_sustainable_woodfuel_guidelines-1-.pdf '''Criteria and indicators for sustainable woodfuels'''] | + | |
− | | + | |
| FAO: 2010 | | FAO: 2010 |
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| This publication assesses the environmental, social and economic issues as<br/>well as the legal and institutional frameworks that can ensure the sustainable<br/>production of woodfuels from forests, trees outside forests and other sources. | | This publication assesses the environmental, social and economic issues as<br/>well as the legal and institutional frameworks that can ensure the sustainable<br/>production of woodfuels from forests, trees outside forests and other sources. |
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| + | | [[File:2010 FAO sustainable woodfuel guidelines-1-.pdf|border|180px|Criteria and indicators for sustainable woodfuels|alt=borderCriteria and indicators for sustainable woodfuels]] |
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− | | <br/> | + | |
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− | '''[http://energypedia.info/index.php/File:FAO_154-Forests_and_energy-2008.pdf Key Issues about Forest and Energy]''' | + | '''[[:File:FAO 154-Forests and energy-2008.pdf|Key Issues about Forest and Energy]]''' |
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| FAO: 2008 | | FAO: 2008 |
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− | General overview of different options to use forest products for energy consumption.<br/>This publication explores questions towards informed policy discussions.<br/>It outlines potential opportunities and impacts in relation to forestry in the context of growing global energy demand. | + | General overview of different options to use forest products for energy consumption.<br/>This publication explores questions towards informed policy discussions.<br/>It outlines potential opportunities and impacts in relation to forestry in the context of growing global energy demand. |
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− |
| + | |
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− | <br/> | + | [[File:FAO 154-Forests and energy-2008.pdf|border|180px|Key Issues about Forests and Energy|alt=Key Issues about Forests and Energy]]<br/> |
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− | The German perspective on wood energy was discussed during an expert meeting in 2010 at GIZ headquarters. German institutions working in the field of wood energy came together for this half-day meeting. | + | The German perspective on wood energy was discussed during an expert meeting in 2010 at GIZ headquarters. German institutions working in the field of wood energy came together for this half-day meeting. |
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| Responsible: GIZ HERA | | Responsible: GIZ HERA |
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− | [http://energypedia.info/index.php/File:GTZ_Expertengespr%C3%A4ch_Holzenergie_12.8.2010_Dokumentation.pdf documentation of results] | + | | [[File:GTZ Expertengespräch Holzenergie 12.8.2010 Dokumentation.pdf|border|180px|Documentation of results|alt=Documentation of results]] |
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| Published by GIZ-HERA – Poverty-oriented Basic Energy Services | | Published by GIZ-HERA – Poverty-oriented Basic Energy Services |
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− | | [[File:2010 0811 GTZ HERA Wood - A source of supply for sustainable energy.pdf|RTENOTITLE]] | + | | [[File:2010 0811 GTZ HERA Wood - A source of supply for sustainable energy.pdf|border|center|180px|GIZ HERA publication : Wood - A source of supply for sustainable energy|alt=GIZ HERA publication : Wood - A source of supply for sustainable energy]] |
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| Author: Geoffrey M. Ndegwa (MSc. Thesis, Cologne, September 2010) | | Author: Geoffrey M. Ndegwa (MSc. Thesis, Cologne, September 2010) |
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| This research highlights the potential in the woodfuel sector to play a key and significant role in the rural and urban poor economic development of Rwanda and Kenya. | | This research highlights the potential in the woodfuel sector to play a key and significant role in the rural and urban poor economic development of Rwanda and Kenya. |
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− | | [[File:Ndegwa2010 Woodfuel Value Chains in Kenya+Rwanda.pdf|RTENOTITLE]] | + | | [[File:Ndegwa2010 Woodfuel Value Chains in Kenya+Rwanda.pdf|border|center|180px|Woodfuel Value Chains in Kenya+Rwanda|alt=Woodfuel Value Chains in Kenya+Rwanda]] |
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| + | '''The wood energy value chain - Opportunity for Development -''' |
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| + | Author: Cornelia Sepp - ECO-Consult |
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| + | | [[File:Wood Energy Value Chain -Oppotunity for Development-.pdf|border|center|120px|Presentation: Wood Energy Value Chain -Oppotunity for Development|alt=Presentation: Wood Energy Value Chain -Oppotunity for Development]]<br/> |
| |} | | |} |
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| + | <br/>[[Woodfuel Production Options#toc|►Go to Top]]<br/> |
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| + | <br/> |
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− | = References<br/> = | + | = References = |
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− | This article was originally published by [http://www.gtz.de/en/themen/12941.htm GIZ HERA]. It is basically based on experiences, lessons learned and information gathered by GIZ cook stove projects. You can find more information about the authors and experts of the original “Cooking Energy Compendium” in the [[Imprint - GIZ HERA Cooking Energy Compendium|Imprint]]. | + | This article was originally published by [http://www.giz.de/fachexpertise/html/2769.html GIZ HERA]. It is basically based on experiences, lessons learned and information gathered by GIZ cook stove projects. You can find more information about the authors and experts of the original “Cooking Energy Compendium” in the [[Imprint - GIZ HERA Cooking Energy Compendium|Imprint]]. |
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− | <references /> | + | <u><references /></u> |
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| + | <br/> |
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| + | [[Woodfuel Production Options#toc|►Go to Top]] |
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− | <font size="2">[[Woodfuel Production Options#Sources_of_Woodfuel|Top of the page]]</font>
| + | [[GIZ HERA Cooking Energy Compendium|--> Back to Overview GIZ HERA Cooking Energy Compendium]]<br/> |
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− | <font size="2">[[GIZ HERA Cooking Energy Compendium|--> Back to Overview GIZ HERA Cooking Energy Compendium]]</font>
| + | {{#set: Hera category=Woodfuel Supply}} |
− | </div>
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− | [[Category:Cooking_Energy_Compendium]] | + | [[Category:Cooking_Energy_Compendium_(GIZ_HERA)]] |
− | [[Category:GIZ_HERA]] | + | [[Category:Woodfuel]] |
| + | [[Category:Madagascar]] |
| + | [[Category:Ethiopia]] |
| + | [[Category:Sub-Saharan_Africa]] |
| [[Category:Wood_Energy]] | | [[Category:Wood_Energy]] |
Woodfuel originates from a wide range of land-use systems. These including agricultural plantations, agroforestry, trees outside forest, tree plantation, secondary forest management, and primary forest management (see table below). The manner in which wood for energy use is produced of course depends on climatic conditions, vegetation cover, local demand, and infrastructure. But it also depends crucially on land ownership (either prviate, communal, state) and land-use rights (including self management, free access, lease, and transfer of user rights) See the figure below for an illustrational overiew.
Planted forests, established through afforestation or reforestation, have a particularly important role to play in providing a renewable and environmentally friendly energy resource.
Currently, there are about 109 million hectares of productive forest plantations in the world. For more information see FAO (2006) "Global Forest Resource Assessment 2005".
In the past, energy plantations were often ill-designed and suffered from insufficient health, vitality, productivity and lacked return on investment. In addition, they were often subject to social and land use conflicts. Many of the plantations failed due to poor management, lack of know-how, and the low commitment of staff in the public forestry services.
Furthermore, there is much controversy about the topic of introduced species versus native specis. It is clear that plantations can be detrimental to biodiversity especially when they are established at the expense of original indigenous forest habitats. Native species should always be given priority. However, the failure of many native species in planting trials regarding growth, resistance to pests, etc, is one of the reasons hindering the wider use of native trees in land rehabilitation. This is often linked to the fact that information on the phenology and silvicultural techniques is lacking, making large scale production in many cases more difficult than with exotics.
With increasing pressure on natural forests, alternative sustainable approaches are needed to keep pace with the growing demand for woodfuel. Rising oil prices keep people from climbing the energy ladder, thus increasing their dependence on woodfuel. Consequently, forest plantations need careful development policies, with public sector dominance giving way to more private sector participation, and integrating with other sectors and approaches to provide a sufficient supply of woodfuel.
Generally, the establishment of plantations on pristine or almost pristine forest lands is not recommended. Hardwood species generally have the greatest potential for woodfuel. The type selected should coppice readily, be a variety that fixes nitrogen, and be a multi-purpose species (meaning a species which can serve several purposes, such as providing fruits, habitat, shade, or soil improvement). Selection also depends on what can be grown easily on the site and what is acceptable to the users. Cultivation methods should be adapted to the skills and resources of the rural people. Care in the establishment phase is very important. Every plantation activity should be preceded by an economic analysis. Sustainability can only be assured when the returns on investment are significant for the plantation owner and have a positive social and ecological potential.
In Madagascar, GIZ adopted a village-based approach of making local people the centre of planning and implementation of woodfuel plantations. Individuals are given the property rights of degraded community land for reforestation. The project provides institutional and technical support, and the soil is initially prepared by tractor before handover. The plantation owner is responsible for raising seedlings and maintaining the plantation. An overall GIS based monitoring system gives data on each and every plantation plot, including productivity figures, income generated, etc. To date (2011), more than 6500 hectares have been planted in Madagascar, providing an increase in income of more than 20% for more than 2000 rural households.
Management of natural forests is a very complex undertaking in areas where the supply of woodfuel is usually a by-product of more valuable products such as timber, poles etc.
Woodfuel shortages generally occur in regions where savannah-type vegetation is predominant due to low and erratic rainfall patterns. These savannah woodlands are not well suited for high-value timber production, although they may make a major contribution to non-timber forest products such as fodder, gums, resins, etc.
The sustainable management of using these savannah woodlands for fuel is often described as Participatory Forest Management (PFM) or Community based forest (natural resources) management.
PFM experienced a particular impetus due to increasing decentralization efforts, in which management responsibility over state-owned forests is increasingly being transfered to local communities. In order to implement a PFM approach and to get local people to invest in sustainable forest management, issues around land tenure and the secure transfer of decision-making powers from central government to local institutions have to be resolved.
-> Recommendations and potential pitfalls around decentralization of natural resources management are described in a publication of the ‘The World Resources Institute’ Democratic Decentralization of Natural Resources
The following features were found to be particularly important when designing and implementing PFM projects for energy supply:
-> Example of an animation tutorial for awareness campaigns: des villages verts. Guide de l'animateur
In Ethiopia, a PFM approach called WAJIB has been developed with GIZ support in which a binding agreement is made between the local forest user groups and the district forest office. There are clearly defined rights, duties and obligations for both partners. This approach differs from many other PFM approaches in Africa as the number of participating households is limited by the forest carrying capacity and the economic potential. The underlying assumption is that households will only invest in forestry operations if they can make a living out of sustainable forest management. Thus, the forest in a given village is subdivided into forest blocks with an average size of 360 hectares. Based on the forest carrying capacity of 12 hectares per household, each block is managed by a WAJIB group of not more than 30 households. Each WAJIB group has its own internal regulations (by-laws), which govern the use, protection, rights and responsibilities of each household within the block. The main duty of the forest administration is to provide technical advice to the WAJIB groups on how to develop and utilize the forest on a sustainable basis.
In Southern Africa, the miombo woodlands are the major sources of fuel. Miombo woodlands are tropical and subtropical grasslands, savannas, and shrublands. These woodlands provide a wide range of products (including timber) and services to rural households, so the forest management approaches need to be very diverse and often embedded in an integrated land use approach. The opportunities and barriers to sustainable management of miombo forests are described in the CIFOR publication Woodlands – Opportunities and Barriers to Sustainable Forest Management 2007.
By harvesting woodfuel, people make an impact on the state of their forests. The impact of these activities on the environment is hard to predict. Ecological monitoring is more and more recognized as a helpful method in natural resource management. The following manual, which discusses community-based ecological monitoring, gives advice to the practitioner of how to conduct such an activity: Community Based Ecological Monitoring.
Although TOFs fulfil a multipurpose function, and are part of an integrated land-use system, woodfuel can be a main product. The FAO (2001) cites references in the Asia-Pacific area, where over two-thirds of the energy demand is supplied by fuelwood from non-forest sources, providing fuel for two billion people.
Trees for fuelwood can be planted dispersed, in a row, on crop land (alley cropping), in home-gardens, as replacement, or by the introduction of selected trees or shrubs to enhance natural fallow vegetation. To control soil and water erosion, trees and shrubs are planted as living barriers along the contour lines of a slope or terrace. Living fences planted as lines of trees on farm boundaries or on pasture plots, animal enclosures or around agricultural fields can contribute to the energy supply of local households. The Agroforestry extension manual for Kenya provides an excellent overview of the different approaches, illustrated by a number of case reports.
As with forest energy plantations, hardwood species that coppice readily and fix nitrogen should be selected (see Table 6) . They should be fast growing hardwoods which can be harvested after 4-6 years, well-adapted to the site, easy to grow, and resistant to goats and wildlife damage. The World Agroforestry Centre maintains a freely accessible database providing information on the management, use and ecology of a wide range of tree species that can be used for fuelwood in agroforestry.
The Sahel Eco-Farm (SEF) approach to agroforestry has been developed with the support of ICRISAT. It is a good example of an agroforestry-based system combining ecological advantages (such as improving microclimate) and soil conditions, with income generation. This approach improves the livelihoods of the rural poor in vulnerable regions such as the Sahel. The SEF is based on an alley cropping system, in which trees and/or shrubs are intercropped with annual crops.[2]
A good example of increasing fuelwood supply is by planting nitrogen-fixing trees that can be harvested for fuelwood or charcoal after 3-4 years as part of a system to improve fallow fields. In Chapter 6 of a recent publication by the World Agroforestry Centre on innovative agroforestry approaches, an improved fallow system is described. See:
-> World Agroforestry into the Future
Enough wood can be obtained from one hectare of improved fallow to supply the fuelwood needs of a typical 6–7 member rural household for 6–8 months.
Another key initiative is to promote agroforestry at policy level so that it is recognized as one of the most important fuelwood supply resources, besides natural forests and plantations. The socio-economic and ecological advantages of agroforestry substantially outweigh many expensive, ill-conceived tree plantation programmes. Agroforestry can be developed at a fraction of the cost of large-scale plantations, and the approach encourages greater local participation and a wider diversity of goods and services for the local and national economies.