Area closure for rehabilitation [Ethiopia]
- Creation:
- Update:
- Compiler: Daniel Danano
- Editor: –
- Reviewers: Donia Mühlematter, Fabian Ottiger
Meret mekelel
technologies_1048 - Ethiopia
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Expand all Collapse all1. General information
1.2 Contact details of resource persons and institutions involved in the assessment and documentation of the Technology
Name of project which facilitated the documentation/ evaluation of the Technology (if relevant)
Book project: where the land is greener - Case Studies and Analysis of Soil and Water Conservation Initiatives Worldwide (where the land is greener)Name of the institution(s) which facilitated the documentation/ evaluation of the Technology (if relevant)
Ministry of Agriculture and Rural Development of Ethiopia (Ministry of Agriculture and Rural Development) - Ethiopia1.3 Conditions regarding the use of data documented through WOCAT
When were the data compiled (in the field)?
01/07/2003
The compiler and key resource person(s) accept the conditions regarding the use of data documented through WOCAT:
Yes
1.4 Declaration on sustainability of the described Technology
Is the Technology described here problematic with regard to land degradation, so that it cannot be declared a sustainable land management technology?
No
2. Description of the SLM Technology
2.1 Short description of the Technology
Definition of the Technology:
Enclosing and protecting an area of degraded land from human use and animal interference, to permit natural rehabilitation, enhanced by additional vegetative and structural conservation measures.
2.2 Detailed description of the Technology
Description:
Area closure involves the protection and resting of severely degraded land to restore its productive capacity. There are two major types of area enclosures practised in Ethiopia: (1) the most common type involves closing of an area from livestock and people so that natural regeneration of the vegetation can take place; (2) the second option comprises closing off degraded land while simultaneously implementing additional measures such as planting of seedlings, mulching and establishing water harvesting structures to enhance and speed up the regeneration process. The focus of this case study is on this second type.
The selection of measures chosen for rehabilitation depends mainly on the land use type, and to a lesser extent on climate, topography and soil type. Degraded croplands with individual land use rights are normally treated with additional structural measures to retain soil moisture and trap sediment, and with agronomic measures to restore soil fertility. Open access grazing lands are closed for natural regeneration while partly treated with additional measures, and open access woodlands are simply closed. In the case study area 60% of the enclosed area is under treatment with additional conservation measures and 40% is under natural regeneration. First, the area to be closed is demarcated and protected with fencing, usually live fences, and a site guard may be assigned to further ensure protection. Structural measures such as micro-basins, trenches, and bunds that enhance water infiltration and soil moisture may be constructed to increase survival rate of vegetative material planted. Hillside terraces, spaced at a 1 m vertical interval with a width of 1 m are constructed on steep slopes (exceeding 20%). Nitrogen-fixing and multipurpose shrubs/trees (for fodder, fuel) such as Acacia saligna, Sesbania sesban, Leucaena leucocephala as well as local grass species such as napier (Pennisetum purpureum) and rhodes (Chloris gayana) are planted as additional measures for conservation.
The maintenance of area enclosures involves activities such as replanting, maintaining of fences, pruning of trees and weeding. After one year, cut-and-carry of grass for stall-feeding can be partly practiced - which is of economic benefit to the farmers. Rehabilitation normally takes about 7-10 years depending on the level of degradation and intensity of management. Land use is limited to selective cutting of trees, collection of dead wood and cut-and-carry of grass for livestock fodder. On individually owned enclosures land users start cutting trees after three years (for eucalyptus) and after 7–8 years (for other trees), while on communal land farmers are allowed to collect dead wood after 3-–4 years, and the community decides about the use of trees.
2.3 Photos of the Technology
2.5 Country/ region/ locations where the Technology has been applied and which are covered by this assessment
Country:
Ethiopia
Region/ State/ Province:
Alaba, South Ethiopia
Further specification of location:
Bilate River Catchment (Rift Valley)
Map
×2.7 Introduction of the Technology
Specify how the Technology was introduced:
- through projects/ external interventions
3. Classification of the SLM Technology
3.1 Main purpose(s) of the Technology
- improve production
- reduce, prevent, restore land degradation
- conserve ecosystem
3.2 Current land use type(s) where the Technology is applied
Mixed (crops/ grazing/ trees), incl. agroforestry
- Silvo-pastoralism
Comments:
Major land use problems (compiler’s opinion): Over 30% of the land in the study area is degraded, resulting in low crop yields and poor livestock production. Severe water erosion is the main cause of land degradation on all slopes, followed by fertility depletion due to intensive cultivation practices and overgrazing. Serious gully formation and a high sediment load in the Bilate River threaten Lake Abaya. Communal grazing lands, woodlands with open access, and cultivated lands on steep slopes without conservation measures are particularly affected. By tradition, land users in rural Ethiopia can own as many livestock as they wish, which encourages overstocking.
Ranching: (before SWC)
Other grazingland: mixed silvo-pastoral (after SWC): cut-and-carry, trees
3.3 Further information about land use
Water supply for the land on which the Technology is applied:
- rainfed
Specify:
Longest growing period in days: 120 Longest growing period from month to month: Jun - Sep
3.4 SLM group to which the Technology belongs
- area closure (stop use, support restoration)
- cross-slope measure
3.5 Spread of the Technology
Comments:
Total area covered by the SLM Technology is 20 m2.
3.6 SLM measures comprising the Technology
3.7 Main types of land degradation addressed by the Technology
soil erosion by water
- Wt: loss of topsoil/ surface erosion
- Wg: gully erosion/ gullying
- Wo: offsite degradation effects
chemical soil deterioration
- Cn: fertility decline and reduced organic matter content (not caused by erosion)
biological degradation
- Bc: reduction of vegetation cover
- Bs: quality and species composition/ diversity decline
Comments:
Main type of degradation addressed: Wt: loss of topsoil / surface erosion, Wg: gully erosion / gullying, Wo: offsite degradation effects, Cn: fertility decline and reduced organic matter content, Bc: reduction of vegetation cover, Bs: quality and species composition /diversity decline
3.8 Prevention, reduction, or restoration of land degradation
Specify the goal of the Technology with regard to land degradation:
- restore/ rehabilitate severely degraded land
4. Technical specifications, implementation activities, inputs, and costs
4.1 Technical drawing of the Technology
4.2 Technical specifications/ explanations of technical drawing
Rehabilitation of degraded land based on enclosure with live fence. Natural regeneration of vegetative cover is supported by water harvesting structures and planting of nitrogen-fixing/multipurpose shrubs and trees as well as local grass species. On steeper slopes hillside terraces may be established.
Technical knowledge required for field staff / advisors: moderate
Technical knowledge required for land users: moderate
Main technical functions: improvement of ground cover, increase of infiltration, control of dispersed runoff, control of concentrated runoff, increase in soil fertility
Secondary technical functions: increase / maintain water stored in soil, less sediment deportation
Mulching
Material/ species: tree leaves/grass
Scattered / dispersed
Vegetative material: T : trees / shrubs
Vegetative measure: oversowing grasses
Vegetative material: G : grass
Vegetative measure: Vegetative material: G : grass
Vegetative measure: Vegetative material: G : grass
Vegetative measure: Vegetative material: G : grass
Trees/ shrubs species: Acacia saligna, Sesbania sesban, Leucaena leucocephala, Eucalyptus spp., Grevillea robusta
Grass species: nepier (Pennisetum purpureum), rhodes (Chloris gayana)
Structural measure: micro-basins (opt.)
Structural measure: terraces (opt.)
Structural measure: bunds (opt.)
Other type of management: land use change, enclosure,, cut-and-carry
4.4 Establishment activities
Activity | Type of measure | Timing | |
---|---|---|---|
1. | Planting of trees (Eucalyptus spp., Grevillea robusta) as well as | Vegetative | (early rainy season). |
2. | Oversowing/interplanting with local grass species: napier grass | Vegetative | (early rainy season). |
3. | Marking the boundary and establishment of live fences: digging pits | Structural | early rainy season (before June). |
4. | Construction of structural measures such as micro- basins, trenches, bunds or hillside terraces. | Structural | before rains |
4.5 Costs and inputs needed for establishment
Specify input | Unit | Quantity | Costs per Unit | Total costs per input | % of costs borne by land users | |
---|---|---|---|---|---|---|
Labour | Labour | ha | 1.0 | 175.0 | 175.0 | 50.0 |
Equipment | Tools | ha | 1.0 | 25.0 | 25.0 | 100.0 |
Plant material | Seeds | ha | 1.0 | 40.0 | 40.0 | |
Plant material | Seedlings | ha | 1.0 | 150.0 | 150.0 | |
Construction material | Stone | ha | 1.0 | |||
Construction material | Wood | ha | 1.0 | |||
Other | site guard (kg grain/ha/year) | ha | 1.0 | 1.0 | 1.0 | 100.0 |
Total costs for establishment of the Technology | 391.0 |
Comments:
Duration of establishment phase: 2 month(s)
4.6 Maintenance/ recurrent activities
Activity | Type of measure | Timing/ frequency | |
---|---|---|---|
1. | Mulching with tree leaves/grass around newly planted trees, before | Agronomic | before rains / initial establishment |
2. | Replanting/gapping up live fence and trees during rains in the early | Vegetative | during rains / |
3. | Harvesting grass | Vegetative | during rainy season. / |
4. | Pruning of trees | Vegetative | in the dry season. / |
5. | Weeding | Vegetative | after rains. / |
6. | Repairing breaks in structures | Structural | before rains./ |
4.7 Costs and inputs needed for maintenance/ recurrent activities (per year)
Specify input | Unit | Quantity | Costs per Unit | Total costs per input | % of costs borne by land users | |
---|---|---|---|---|---|---|
Labour | Labour | ha | 1.0 | 35.0 | 35.0 | 100.0 |
Equipment | Tools | ha | 1.0 | 5.0 | 5.0 | 100.0 |
Plant material | Seeds | ha | 1.0 | 10.0 | 10.0 | |
Plant material | Seedlings | ha | 1.0 | 40.0 | 40.0 | |
Other | site guard (kg grain/ha/year) | ha | 1.0 | 1.0 | 1.0 | 100.0 |
Total costs for maintenance of the Technology | 91.0 |
Comments:
Labour for establishment activities: 250 person days per ha for structural measures and planting of trees, plus guarding. Labour for maintenance: 50 person days for replanting/weeding. A common daily wage is US$ 0.70 (= 6 Ethiopian Birr), however in this case the site guards were given 3 kg of grains per ha per year. They can control over 200 ha.
5. Natural and human environment
5.1 Climate
Annual rainfall
- < 250 mm
- 251-500 mm
- 501-750 mm
- 751-1,000 mm
- 1,001-1,500 mm
- 1,501-2,000 mm
- 2,001-3,000 mm
- 3,001-4,000 mm
- > 4,000 mm
Specifications/ comments on rainfall:
751-1,000 mm (ranked 1)
1,001-1,500 mm (ranked 2)
Agro-climatic zone
- sub-humid
Thermal climate class: tropics
5.2 Topography
Slopes on average:
- flat (0-2%)
- gentle (3-5%)
- moderate (6-10%)
- rolling (11-15%)
- hilly (16-30%)
- steep (31-60%)
- very steep (>60%)
Landforms:
- plateau/plains
- ridges
- mountain slopes
- hill slopes
- footslopes
- valley floors
Altitudinal zone:
- 0-100 m a.s.l.
- 101-500 m a.s.l.
- 501-1,000 m a.s.l.
- 1,001-1,500 m a.s.l.
- 1,501-2,000 m a.s.l.
- 2,001-2,500 m a.s.l.
- 2,501-3,000 m a.s.l.
- 3,001-4,000 m a.s.l.
- > 4,000 m a.s.l.
Comments and further specifications on topography:
Altitudinal zone: Also 1,001-1,500 m a.s.l. (ranked 2) and 2001-2500 m a.s.l. (ranked 3)
Slopes on average: Also hilly (ranked 2) and moderate (ranked 3)
5.3 Soils
Soil depth on average:
- very shallow (0-20 cm)
- shallow (21-50 cm)
- moderately deep (51-80 cm)
- deep (81-120 cm)
- very deep (> 120 cm)
Soil texture (topsoil):
- coarse/ light (sandy)
- medium (loamy, silty)
Topsoil organic matter:
- low (<1%)
If available, attach full soil description or specify the available information, e.g. soil type, soil PH/ acidity, Cation Exchange Capacity, nitrogen, salinity etc.
Soil depth on average: Also moderately deep (ranked 2) and deep (ranked 3)
Soil fertility: Low
Topsoil organic matter: Also medium and high (both ranked 2)
Soil drainage/infiltration: Good
Soil water storage capacity: Very high
5.6 Characteristics of land users applying the Technology
Market orientation of production system:
- subsistence (self-supply)
Off-farm income:
- less than 10% of all income
Indicate other relevant characteristics of the land users:
Off-farm income specification: from petty trade, weaving, etc
5.7 Average area of land owned or leased by land users applying the Technology
- < 0.5 ha
- 0.5-1 ha
- 1-2 ha
- 2-5 ha
- 5-15 ha
- 15-50 ha
- 50-100 ha
- 100-500 ha
- 500-1,000 ha
- 1,000-10,000 ha
- > 10,000 ha
5.8 Land ownership, land use rights, and water use rights
Land ownership:
- state
Land use rights:
- open access (unorganized)
- individual
6. Impacts and concluding statements
6.1 On-site impacts the Technology has shown
Socio-economic impacts
Production
fodder production
Comments/ specify:
(cut-and-carry of grass)
fodder quality
Comments/ specify:
(cut-and-carry of grass)
wood production
production area
Comments/ specify:
Reduction of grazing area leads to high pressure on remaining grazing areas
Income and costs
expenses on agricultural inputs
farm income
Comments/ specify:
(selling grass/wood)
workload
Socio-cultural impacts
community institutions
SLM/ land degradation knowledge
conflict mitigation
Comments/ specify:
Unequal share of benefits, some illegal cutting of vegetation is involved
Ecological impacts
Water cycle/ runoff
excess water drainage
Soil
soil moisture
Comments/ specify:
>50%
soil cover
Comments/ specify:
>80%
soil loss
Comments/ specify:
initially 50% reduction, after 2–3 years
Other ecological impacts
Soil fertility
Comments/ specify:
increased organic matter, nitrogen fixing shrubs
Biodiversity
Comments/ specify:
recovering disappearing local species
competition between (grass)species
Comments/ specify:
competition between naturally regenerating and oversown (grass)species
6.2 Off-site impacts the Technology has shown
reliable and stable stream flows in dry season
Comments/ specify:
Also groundwater recharge
downstream flooding
downstream siltation
Comments/ specify:
Less sediment transported
groundwater/ river pollution
6.4 Cost-benefit analysis
How do the benefits compare with the establishment costs (from land users’ perspective)?
Short-term returns:
positive
Long-term returns:
very positive
How do the benefits compare with the maintenance/ recurrent costs (from land users' perspective)?
Short-term returns:
positive
Long-term returns:
very positive
6.5 Adoption of the Technology
Of all those who have adopted the Technology, how many have did so spontaneously, i.e. without receiving any material incentives/ payments?
- 90-100%
Comments:
300 land user families have adopted the Technology with external material support
90% of land user families have adopted the Technology without any external material support
There is a moderate trend towards spontaneous adoption of the Technology
Comments on adoption trend: Adoption rate has considerably increased owing to improved ownership feeling and immense benefits obtained through the practice. However, if labour-intensive structural measures are required people rely on food-for-work incentives.
6.7 Strengths/ advantages/ opportunities of the Technology
Strengths/ advantages/ opportunities in the compiler’s or other key resource person’s view |
---|
Reduction of on-site and off-site land degradation, reclamation of degraded non-productive land (regenerating fertility) How can they be sustained / enhanced? Strengthen maintenance and protection to increase biomass production of enclosure. |
Fodder shortage is reduced through cut-and-carry of grass in enclosures (after 1 year) How can they be sustained / enhanced? Introduce more productive and nutritious grass/legume species. |
Collection of dead wood from enclosures (after 3–4 years) mitigates fuelwood shortage How can they be sustained / enhanced? Introduce alternative fast growing multi-purpose tree species such as Grevillea robusta (fodder for smallstock in very dry periods). |
Cutting wood for construction of houses and wooden farm implements (after 7–8 years) How can they be sustained / enhanced? Continue planting of multipurpose trees. |
Increased honey production through increased bee activity in enclosures Emerge of springs, which have disappeared due to deforestation/land degradation Income generation: farmers sell grass/wood collected from area enclosures; they make profit despite seven years enclosure How can they be sustained / enhanced? Improve beehives, ‘bee feed’ (bee-friendly plants), and access to market. Maintain proper ground cover to improve infiltration and percolation of rainwater. Better management of planted grass, making of hay, improve market systems. |
Emergence of springs, which have disappeared due to deforestation/land degradation -> Maintain proper ground cover to improve infiltration and percolation of rainwater. - Income generation: farmers sell grass/wood collected from area enclosures; they make profit despite seven years enclosure -> Better management of planted grass, making of hay, improve market systems. Editors’ comments: Protecting degraded land against grazing is a common practice worldwide. In Ethiopia it is the second most important SWC practice after structural conservation measures. About 1.2 million hectares of degraded lands have been closed for rehabilitation in Ethiopia during the past three decades. As this case study shows, results are encouraging both in terms of effective protection and enhanced production. Land use rights: open access on woodlands and grazing lands (communal land use rights), individual on cropland |
6.8 Weaknesses/ disadvantages/ risks of the Technology and ways of overcoming them
Weaknesses/ disadvantages/ risks in the compiler’s or other key resource person’s view | How can they be overcome? |
---|---|
On highly eroded areas and in areas with low rainfall the survival rate of trees and shrubs is low and as a result the benefits only come after a very long period. This situation becomes unacceptable to the land users |
Select suitable local and exotic multipurpose tree/shrub species adapted to the local conditions (Acacia spp., Eucalyptus spp., Grevillea robusta etc). Construct water-harvesting structures (trenches, micro-basins). Raise awareness among land users through meetings and training. |
Investment costs are rather high for land users | Credits, loans, cooperatives. |
Inequitable share of benefits | Awareness should be increased through enhancing the LLPP approach. |
7. References and links
7.2 References to available publications
Title, author, year, ISBN:
Chadokar PA: Multipurpose Plant Species for Soil and Water Conservation. Assistance to Soil and Water ConservationProgramme. ETH/81/003. 1985.
Title, author, year, ISBN:
Betru Nedassa: Biological Soil Conservation Measures. Land Rehabilitation and Reforestation Project. Project 2488MOA/WFP. 1995.
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