Firebreaks [Niger]
- Creation:
- Update:
- Compiler: Soumaila Abdoulaye
- Editor: –
- Reviewers: Alexandra Gavilano, Simone Verzandvoort, Rima Mekdaschi Studer, Joana Eichenberger
technologies_2323 - Niger
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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
SLM specialist:
Abdoulaye Mahamane
NGO Association for Rural Development (ADR)
Niger
1.3 Conditions regarding the use of data documented through WOCAT
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
Comments:
This technology is a measure for the sustainable management of grazing land, in accordance with the national and international standards.
2. Description of the SLM Technology
2.1 Short description of the Technology
Definition of the Technology:
Firebreaks are strips from which dry vegetation – straw - is removed in order to stop the progression of fire into the large areas of grazing land. They are of paramount importance for protecting and securing available grazing.
2.2 Detailed description of the Technology
Description:
In Niger, firebreaks are constructed in pastoral and agropastoral zones, which are characterized by abundant grazing after the rainy season – but also by a high risk of bush fires. Every year, at the end of the rainy season, thousands of hectares of grazing land go up in smoke due to bush-fires. This causes enormous losses of fodder, which is essential for the survival of livestock in this Sahelian region which has lacked adequate grazing over the last decades.
Firebreaks, as their name indicates, are strips of land set-up perpendicular to the dominant wind direction. They are between 20 and 30 m in width and spaced 3 to 4 km apart - according to the national standards in Niger. Along these strips, which can exceed 10 km in length in the pastoral zones, dried vegetation is removed. This creates firebreaks which stop the progression of fires into the large areas of grazing, thereby protecting and securing fodder supplies. In general, firebreaks are implemented according to a “cash for work” approach, with the aim of supporting the local economy and strengthening the resilience of the population, and of the livestock, during the lean season. Three specific objectives are set for this technology in Niger: (i) the clearance of the firebreaks is part of the annual plan for preliminary support to the populations experiencing food insecurity. These plans are implemented by the National Mechanism for the Prevention and Management of Disasters and Food Crises (DNPGCCA). This is an instrument to distribute income and food supplies to populations through the work carried out under the initiative termed “High-Intensity Labour” (HIMO), through the “work for food supplies and/or cash” approach; (ii) the selling of the straw was developed to enable people on the one hand to increase their financial resources, and on the other hand to implement strategies for storage and optimal use of the fodder resources; (iii) finally, the firebreaks provide the opportunity to ensure first, information delivery and awareness-raising amongst the local people about sustainable land management, second, the training of fire guards and livestock keepers in sustainable management of fodder resources, and third, the spatial planning of the grazing areas, with the aim of securing the movement of transhumant herds.
The main activity in the implementation and maintenance of the firebreaks is weeding with local tools (Hilaire, daba, machete) and the collection and storage of the cut straw. These activities require a large number of laborers (men and women). The main advantages of the technology are low implementation costs, ease of scaling-up, contribution to efficient management of the fodder resources, and a contribution to the training/mobilization/ organization of the pastoralist populations. Finally, it fosters efficient spatial planning of the grazing areas. The direct impacts are reduction of bushfires, improved protection of grazing areas, and an increase in the income of the local people. The indirect impacts consist of the increased financial resources of the land users, and the impacts of the measures for the prevention, and management, of disasters and food crises.
This technology, while combating bushfires and fostering the increase of incomes, contributes to improved livelihoods of livestock keepers and to sustainable land management. However, the systematic commercialization of the cut straw may reduce the potential for regeneration of the vegetation cover in the grazing areas, and may cause conflicts between the traders of straw and the land users.
2.3 Photos of the Technology
General remarks regarding photos:
These pictures show the implementation of the technology in several regions in Niger. They allow to understand the technical management of the sustainable land management measure, both in the agro-pastoral and pastoral zones. The pictures also show that the local population is organized in the implementation of these works.
2.4 Videos of the Technology
Comments, short description:
No video is available yet.
2.5 Country/ region/ locations where the Technology has been applied and which are covered by this assessment
Country:
Niger
Region/ State/ Province:
Urban municipality of Abalak, Department of Abalak, Region of Tahoua
Further specification of location:
Grazing area of Ameidida (40 km southwest of Abalak)
Specify the spread of the Technology:
- evenly spread over an area
If the Technology is evenly spread over an area, specify area covered (in km2):
3.0
If precise area is not known, indicate approximate area covered:
- 1-10 km2
Comments:
The sites of the firebreaks are located in Ameidida, southwest of Abalak (40 km from Abalak).
The firebreaks are constructed perpendicularly to the dominant wind direction, with a spacing between the structures of 3 km to 4 km. The width of each strip is between 20 m and 30 m. The length of the strips varies depending on the length of the zone to protect. In the pastoral zone, the length can exceed 10 km. Finally, this technology is applied in pastoral areas (sylvo-pastoral or agro-sylvo-pastoral land). In the case of Ameidida, the surface covered by the firebreaks is 3 km2. The total treated area is 363 km2, including the areas between the firebreaks.
Map
×2.6 Date of implementation
Indicate year of implementation:
2016
2.7 Introduction of the Technology
Specify how the Technology was introduced:
- through projects/ external interventions
Comments (type of project, etc.):
The project concerned is a micro-project, financed by the Food Crisis Unit (CCA/the Prime Minister's Office), in the framework of the Annual Plan to Support Vulnerable Populations. The CCA/Prime Minister's Office is an institution of the DNPGCCA.
3. Classification of the SLM Technology
3.1 Main purpose(s) of the Technology
- reduce, prevent, restore land degradation
- conserve ecosystem
- preserve/ improve biodiversity
- reduce risk of disasters
- create beneficial economic impact
- create beneficial social impact
- ) The clearance of the firebreaks is part of the annual plan for preliminary support to the populations experiencing food insecurity. It is an instrument to distribute income and food supplies to people through the work accomplished under the “High-Intensity Labour” (HIMO) initiative through the approach of “work for food supplies and/or cash”. (ii) Selling of the straw was developed to enable people on the one hand to increase their financial resources, and on the other hand to implement strategies for storage and optimal use of the fodder resources. (iii) The firebreaks provide the opportunity to ensure information and awareness-raising of the people about sustainable land management. This includes the training of fire guards and livestock keepers in sustainable management of fodder resources, and spatial planning of the grazing areas, with the aim of securing the movement of transhumant herds.
3.2 Current land use type(s) where the Technology is applied
Land use mixed within the same land unit:
Yes
Specify mixed land use (crops/ grazing/ trees):
- Agro-silvopastoralism
Cropland
- Annual cropping
- Tree and shrub cropping
Annual cropping - Specify crops:
- cereals - millet
- cereals - sorghum
- vegetables - leafy vegetables (salads, cabbage, spinach, other)
- root/tuber crops - potatoes
- tomatoes
Tree and shrub cropping - Specify crops:
- citrus
- mango, mangosteen, guava
Number of growing seasons per year:
- 1
Specify:
Rainfed crops are grown on small surfaces, including cereals (millet, sorghum) and cowpea. The rainy season occurs from June to September.These crops are prohibited by law. Likewise, the horticultural production, which develops during the dry and cool season, is contrary to existing regulations. But this agricultural production is allowed because of the almost chronic situation of food insecurity in this zone since several decades.
Grazing land
Extensive grazing:
- Nomadism
- Semi-nomadic pastoralism
Animal type:
- goats
- camels
- horses
- mules and asses
- sheep
- cattle
Comments:
Main animal species and products: In the pastoral zone of Abalak, the main animal breeds are cattle, camels, sheep, goats, mules and horses. The latter (horses) are becoming increasingly rare. Mules are mainly kept by Peulh (Bororo) and by some Tuareg.
Main products/ services: A small number of livestock keepers practice rainfed agriculture by producing sorghum and millet. In the lower parts of the landscape, several livestock keepers practice horticulture by producing vegetables (tomatoes, lettuce), potatoes and various fruits (mango, lemon, etc.). Over the past twenty years, irrigated agriculture has seen a spectacular development due to the implementation of adaptation strategies for climate change.
The pastoral zone in the region of Abalak is part of the northern pastoral zone of Tahoua, where agriculture is prohibited. But the local populations and the Hausa coming from the south increasingly produce millet, sorghum and cowpea on small surfaces. Likewise, in response to climate change, several livestock keepers have switched to horticulture, along with the development of irrigated horticulture in this region, which is oriented exclusively on pastoralism. Consequently, at the end of the years 2000, private ranches appeared, which tried to establish semi-ranching by fencing hundreds of hectares. These ranches, belonging to politicians or officers from the Nigerian army, are in breach with the regulation on pastoralism of 2010. In one of the cases, the FAO has supported this private initiative, which challenges the free access to grazing areas by the populations.
Livestock density: The livestock numbers (in tropical livestock units) are between 200,000 and 300,000 over the five last years, which is high considering the overall area and the human population dependent on them.
3.3 Has land use changed due to the implementation of the Technology?
Has land use changed due to the implementation of the Technology?
- No (Continue with question 3.4)
Comments:
The land use has not changed due to the implementation of the technology. In contrast, it has generated the marketing of the straw, which brings income to the livestock keepers’ organisations. It should be noted that more and more livestock keepers are developing irrigated horticulture in depressions and in the valley bottoms, because they have lost almost their entire herds after the droughts of the last thirty years.
3.4 Water supply
Water supply for the land on which the Technology is applied:
- mixed rainfed-irrigated
Comments:
The pastoral zone of Abalak receives less than 300 mm of rain per year on average. These rains, which occur over the period from June to September, cause the formation of temporary ponds, and enable the recharge of the groundwater. In the depressions and valley bottoms, several livestock keepers practice horticulture with a traditional irrigation system (camels are used as traction animals to supply the water).
3.5 SLM group to which the Technology belongs
- pastoralism and grazing land management
- protection and securing grazing land
3.6 SLM measures comprising the Technology
vegetative measures
- V3: Clearing of vegetation
other measures
Comments:
The firebreaks are vegetative measures, but their adaptations go beyond vegetative measures.
3.7 Main types of land degradation addressed by the Technology
biological degradation
- Bc: reduction of vegetation cover
- Bq: quantity/ biomass decline
- Bf: detrimental effects of fires
Comments:
The firebreaks contribute to limiting the effects of bush fires on the vegetation cover and the biomass.
3.8 Prevention, reduction, or restoration of land degradation
Specify the goal of the Technology with regard to land degradation:
- prevent land degradation
- reduce land degradation
Comments:
The firebreaks contribute firstly to preventing effects from bush fires on the available grazing land, by mobilizing the local populations in regular activities of surveillance, monitoring and control of the bush fires in the grazing areas, and in imposing penalties to those responsible for the bush fires. Secondly, in case of bush fires, the effects for grazing are limited; the firebreaks therefore reduce the land degradation which would result from these bush fires.
4. Technical specifications, implementation activities, inputs, and costs
4.1 Technical drawing of the Technology
Technical specifications (related to technical drawing):
The drawing shows ten firebreaks, each with a width of between 20 m and 30 m, a length of 10 km (in this case for the pastoral zone), and a spacing of 3 km to 4 km between them. The firebreaks are perpendicular to the dominant wind direction, which is from east to west in Niger. In the agro-pastoral zones, the length of the firebreaks is below 10 km.
Author:
Abdoulaye Sambo Soumaila
Date:
21/06/2017
4.2 General information regarding the calculation of inputs and costs
Specify how costs and inputs were calculated:
- per Technology area
Indicate size and area unit:
3 km2
other/ national currency (specify):
West African CFA franc
If relevant, indicate exchange rate from USD to local currency (e.g. 1 USD = 79.9 Brazilian Real): 1 USD =:
500.0
Indicate average wage cost of hired labour per day:
1300 CFA francs
4.3 Establishment activities
Activity | Timing (season) | |
---|---|---|
1. | Information/awareness-raising/mobilization of the local populations | At the start of the project, after the harvest and the clearing of the fields in the agro-pastoral zone. In the pastoral zone, this activity is after the end of the rainy season. |
2. | Planning workshop to identify the direct beneficiaries | After the campaign of information/awareness-raising/mobilization of the local populations, during one day |
3. | Training of fire guards | After the identification of direct beneficiaries, over three days. |
4. | Laying-out of the firebreaks | After the rainy season and following the training of fire guards. |
5. | Weeding | After the laying-out the firebreaks. |
6. | Collection, transport and storage of the straw | At the same time as weeding of the outlined strips. |
7. | Selling of the straw on the markets | During the lean season (March-June). |
8. | Monitoring and evaluation | During the period of implementation of the technology, and after the end of the project. |
Comments:
The main activities in the implementation of the firebreaks are the weeding, the collection and the storage of the straw. In some cases, the straw is distributed between the livestock keepers (direct beneficiaries), who use it for their livestock. Monitoring and evaluation are carried out by the local contracting NGO, the technical departmental services, and by members of the sub-regional committee for the prevention and management of food crises (agriculture, livestock keeping, environment).
4.4 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 provided by direct beneficiaries of 'cash for work' | person-days | 100.0 | 50000.0 | 5000000.0 | |
Labour | Technical trainers | person-days | 2.0 | 50000.0 | 100000.0 | |
Labour | Technical surveyors | person-days | 180.0 | 1300.0 | 234000.0 | |
Labour | Supervision-monitoring | person-days | 24.0 | 10000.0 | 240000.0 | |
Equipment | Information/awareness-raising | person-days | 6.0 | 10000.0 | 60000.0 | |
Equipment | Drivers | person-days | 16.0 | 7000.0 | 112000.0 | |
Equipment | Supervisors | person-days | 4.0 | 50000.0 | 200000.0 | |
Equipment | Monitoring by the Chairman/Sub-regional Committee/Program for the Management of Disasters and Food crises, and by the municipality | person-days | 4.0 | 25000.0 | 100000.0 | |
Equipment | Tools for weeding (scythes, rakes, machetes, 'daba', shovels) | km | 100.0 | 13475.0 | 1347500.0 | |
Equipment | Mule/oxen carts | number | 10.0 | 20000.0 | 200000.0 | 100.0 |
Other | Fuel | litre | 1350.0 | 540.0 | 729000.0 | |
Other | Support for trainees | person-days | 15.0 | 6500.0 | 97500.0 | |
Other | Administrative costs | fixed price (5%) | 1.0 | 411000.0 | 411000.0 | |
Total costs for establishment of the Technology | 8831000.0 | |||||
Total costs for establishment of the Technology in USD | 17662.0 |
If you are unable to break down the costs in the table above, give an estimation of the total costs of establishing the Technology:
8831000.0
If land user bore less than 100% of costs, indicate who covered the remaining costs:
The mule and oxen carts for the transport of the straw were provided by the local populations. In the cost assessment, the 20.000 CFA francs represent the rental cost for each cart.
Comments:
The firebreaks are implemented in the framework of the annual plans to support vulnerable populations in all regions of Niger. They are realized with the approach 'cash for work' after the rainy season. In a few cases, the firebreaks are cleared during the rainy season. This is not according to the national standards and does not fit in the framework of sustainable land management. Ultimately, all costs are covered by the Food Crisis Unit, except for the costs for the use of mule and oxen carts, which are owned by the direct beneficiaries.
4.5 Maintenance/ recurrent activities
Activity | Timing/ frequency | |
---|---|---|
1. | Weeding | Once a year after the rainy season |
2. | Collection and storage of the straw | Once a year after the rainy season |
3. | Selling of the straw | Continuously during the lean season |
Comments:
The maintenance activities consist of weeding the strips after each rainy season. This activity should be continuously performed during the entire period of high fire risk in the agro-pastoral and pastoral zones (October-February).
4.6 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 | Unskilled labour | person-days | 100.0 | 5000.0 | 500000.0 | 100.0 |
Labour | Fire guards | person-days | 150.0 | 1300.0 | 195000.0 | 100.0 |
Equipment | Small equipment (rakes, scythes, pitchforks, etc.) | km | 100.0 | 1347.5 | 134750.0 | 100.0 |
Equipment | Mule/oxen carts | number | 10.0 | 20000.0 | 200000.0 | 100.0 |
Total costs for maintenance of the Technology | 1029750.0 | |||||
Total costs for maintenance of the Technology in USD | 2059.5 |
If you are unable to break down the costs in the table above, give an estimation of the total costs of maintaining the Technology:
1029750.0
If land user bore less than 100% of costs, indicate who covered the remaining costs:
The maintenance costs are covered by the local populations, who ensure their own compensation by selling the straw.
Comments:
The success of the maintenance is highly dependent on the income that is generated with the sale of the straw. Therefore, the livestock keepers organize themselves to maintain the firebreaks, which are used as corridors and rest areas in the majority of cases. These costs are calculated for each unit of 3 km2.
4.7 Most important factors affecting the costs
Describe the most determinate factors affecting the costs:
The most important factor affecting the costs of the technology is unskilled labour; this technology requires a large amount of labour, both for the implementation and for the maintenance.
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
Specify average annual rainfall (if known), in mm:
299.00
Specifications/ comments on rainfall:
The department of Abalak is situated in the pastoral zone north of the region of Tahoua. The precipitation in this zone is below 300 mm (extremes: 194 mm in 1984 and 474 mm in 1994), and occurs in general from June to September (20 to 36 rainy days per year). This region has a Sahelo-Saharan climate, and is experiencing the effects of climate change. The amount of precipitation in the region has been decreasing significantly for several decades . The process of desertification has accelerated in this department. This forces the population to shift to irrigated horticulture.
Indicate the name of the reference meteorological station considered:
Abalak prefecture
Agro-climatic zone
- semi-arid
The site of Ameidida is located in the macro-agro-ecological zone of Azouagh. This is an exclusively pastoral region, characterized by low rainfall and a semi-desert climate (high day temperatures, sand storms, etc.) of Sahelian-Saharan type. However, irrigated agriculture is developing in the valleys and the depressions with fertile soils.
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.
Indicate if the Technology is specifically applied in:
- not relevant
Comments and further specifications on topography:
The firebreaks are constructed in the grazing areas, generally on flat or gently sloping terrain. These regions consist of plateaus/glacis, plains and valleys. Several sand dunes have formed over the last four decades.
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)
Soil texture (> 20 cm below surface):
- coarse/ light (sandy)
- medium (loamy, silty)
Topsoil organic matter:
- medium (1-3%)
If available, attach full soil description or specify the available information, e.g. soil type, soil PH/ acidity, Cation Exchange Capacity, nitrogen, salinity etc.
There are two main soil types: (i) sandy soils and sandy-loam soils in the dune formations, and (ii) clay soils and loamy clay soils in the valleys and depressions. On the hillslopes glacis and stony soils are found.
5.4 Water availability and quality
Ground water table:
> 50 m
Availability of surface water:
medium
Water quality (untreated):
poor drinking water (treatment required)
Is water salinity a problem?
No
Is flooding of the area occurring?
No
Comments and further specifications on water quality and quantity:
The populations generally use water from the ponds and from the wells of the pastoralists. Despite the low quality of the water in the ponds, the pastoralist populations (transhumants and nomads) use the water for their daily consumption. This is because there is only a small number of wells in this region, where the groundwater is at more than 100 m depth. A water divide separates the department in two parts: in the west, the groundwater depth is more than 300 metres, which requires the construction of pumping stations, and in the east the groundwater is found at smaller depths (less than 300 m). But in the valleys and depressions, water can be found at smaller depths (lower than 100 m). In the areas with horticulture, dromedaries are generally used as traction animals to pump up the water. At some wells donkeys are used.
5.5 Biodiversity
Species diversity:
- low
Habitat diversity:
- low
Comments and further specifications on biodiversity:
The vegetation consists of the herbaceous and shrub layers. The herbaceous layer is dominated by the species Cenchrus biflorus, Eragrostis atrovirens, et Tribulus terrestris. Also found are species like Blepharis linarifolia, Cyperus conglomeratus, and Cymbopogon schoenantus, which are disappearing. The tree layer consists mainly of thorny plants: Acacia raddiana, Acacia ehrenbergiana, Balanites aegyptiaca and Maerua crassifolia.
The wildlife used to be abundant and varied. Nowadays, it is reduced to several species of bustards, jackals, foxes, hares and guinea fowls. Birds are the most varied and numerous species. They comprise aquatic and terrestrial species. Reptiles and rodents are also numerous.
5.6 Characteristics of land users applying the Technology
Sedentary or nomadic:
- Semi-nomadic
- Nomadic
Market orientation of production system:
- subsistence (self-supply)
- mixed (subsistence/ commercial)
Off-farm income:
- less than 10% of all income
- 10-50% of all income
Relative level of wealth:
- very poor
- poor
Individuals or groups:
- individual/ household
- groups/ community
Level of mechanization:
- manual work
- animal traction
Gender:
- women
- men
Age of land users:
- youth
- middle-aged
Indicate other relevant characteristics of the land users:
The majority of the population are Tuareg. The Bororo Peulh are the second most important ethnical group. Tuareg and Bororo Peulh are nomadic or semi-nomadic livestock keepers which own most of the herds in the region. Also present are some Hausa people who have come from the south to do manual labour, and who cultivate a few patches of land in the rainy season. In the process of transhumance, whole families participate in the implementation of the activities: women, men and children. Only older people and infants do not participate in the work.
5.7 Average area of land used 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
Is this considered small-, medium- or large-scale (referring to local context)?
- small-scale
- medium-scale
Comments:
In the pastoral zone, private land ownership does not exist according to the law. The livestock keepers install themselves on the lands and cultivate these. However, private ranches increasingly appear in this zone, challenging the socio-economic and environmental equilibrium.
5.8 Land ownership, land use rights, and water use rights
Land ownership:
- state
- communal/ village
Land use rights:
- open access (unorganized)
- communal (organized)
Water use rights:
- open access (unorganized)
- communal (organized)
Comments:
In the pastoral zone, the grazing land was declared communal by the scheme on pastoralism of 2010. Private land ownership in this zone does not exist according to the law. The scheme of 2010 regulates the access to resources (water and grazing land). It should be noted that private land ownership only exists in agglomerations and urban centres.
5.9 Access to services and infrastructure
health:
- poor
- moderate
- good
education:
- poor
- moderate
- good
technical assistance:
- poor
- moderate
- good
employment (e.g. off-farm):
- poor
- moderate
- good
markets:
- poor
- moderate
- good
energy:
- poor
- moderate
- good
roads and transport:
- poor
- moderate
- good
drinking water and sanitation:
- poor
- moderate
- good
financial services:
- poor
- moderate
- good
6. Impacts and concluding statements
6.1 On-site impacts the Technology has shown
Socio-economic impacts
Production
fodder production
Quantity before SLM:
0
Quantity after SLM:
100%
Comments/ specify:
The production of fodder intended for marketing has significantly increased, by more than 100%. As a result, the income of the local populations besides the livestock keeping has increased significantly. The clearing of the firebreaks has not had negative effects on the natural production of fodder. However, some studies show that in the long term, dynamics of soil degradation on the strips could result in a significant reduction of the land productivity.
fodder quality
Quantity before SLM:
0
Quantity after SLM:
uncertain
Comments/ specify:
The quality of the fodder could be reduced due to the weeding and storage of the straw (bad conditions of transport and storage). Therefore, the quality could be increased by conservation measures around the firebreaks (on-site fodder quality).
animal production
Quantity before SLM:
0
Quantity after SLM:
uncertain
Comments/ specify:
According to some development projects which promoted firebreaks, these structures could foster intensification of the animal production. The availability of straw throughout the year is an important factor in increasing the animal production in this Nigerian livestock breeding system. But the intensification of production is still weak and cannot be considered significant.
Income and costs
diversity of income sources
Quantity before SLM:
0
Quantity after SLM:
200.000 CFA francs to 1.000.000 francs CFA per site and per year
Comments/ specify:
The implementation of the technology enables a significant increase of income, in particular resulting from the sale of straw.
Socio-cultural impacts
community institutions
Quantity before SLM:
0
Quantity after SLM:
A committee of fire guards is installed in each site.
Comments/ specify:
Following the implementation of the firebreaks, the fire guards were committed to attend to compliance with the regulations in force on the treated sites.
national institutions
Quantity before SLM:
0
Quantity after SLM:
All the national institutions are involved every year at the municipalities, the departments and the regions.
Comments/ specify:
The member institutions of the National Mechanism for the Prevention and Management of Disasters and Food Crises (at the level of the departments and the municipalities) are involved in the monitoring and evaluation of the vulnerability of the populations, and especially in monitoring progress. The land commissions attend to the compliance with the legislation of the rural code.
SLM/ land degradation knowledge
Quantity before SLM:
0
Quantity after SLM:
100%
Comments/ specify:
Training, and especially the campaigns for informing/awareness-raising/mobilizing the livestock keepers have ensured the strengthening of capacities of the local populations in the field of sustainable land management.
conflict mitigation
Quantity after SLM:
depending on the zones
Comments/ specify:
The clearing of the firebreaks enables to recall the regulations in force. The deployment of fire guards mobilizes all stakeholders for natural resource management. This increases dialogue and improves the peaceful co-existence in the zone. However, in the agro-pastoral zone, the pressure on resources leads to conflicts between the agro-pastoralists and the young traders of straw.
situation of socially and economically disadvantaged groups
Quantity before SLM:
0
Quantity after SLM:
100%
Comments/ specify:
The approach of “cash for work” for vulnerable people contributes to improving the situation of socially and economically disadvantaged groups. In this zone, slavery-like practices were developed by some traditional authorities, and criticized by several NGOs. These practices consisted of putting groups to work, and transferring their wages to their “masters”. These practices are disappearing in the zone.
Ecological impacts
Water cycle/ runoff
surface runoff
Quantity before SLM:
0
Quantity after SLM:
20%
Comments/ specify:
The firebreaks are bare areas, on which surface runoff could be increased. It is estimated that surface runoff could increase to at least 20% after the clearing of a firebreak.
Soil
soil cover
Quantity after SLM:
5%
Comments/ specify:
The technology consists of clearing the soil in the firebreaks, which reduces the vegetation cover on the site. This could promote some forms of erosion (mainly water erosion). This should be taken into account in the maintenance of the firebreaks.
Climate and disaster risk reduction
fire risk
Quantity before SLM:
11 fires before the implementation of the technology
Quantity after SLM:
0 fires after the implementation of the technology
Comments/ specify:
The technology is intended to reduce the fire risk and to protect a part of the grazing areas in case of bush fires. Since the implementation of the technology and the establishment of the team of fire guards, no bush fires were observed in the zone.
6.2 Off-site impacts the Technology has shown
water and wind erosion
Quantity before SLM:
0
Quantity after SLM:
10%
Comments/ specify:
The weeding of the firebreaks could increase the risk of water erosion due to surface runoff in the weeded part. The loss of vegetation cover in some parts of the grazing areas could also promote wind erosion, with sand from outside the sites being transported to the treated zones.
Specify assessment of off-site impacts (measurements):
The firebreaks have small off-site impacts. It should be noted that the transport of the straw leads to the movement of some forage seeds to other zones, where they could become invasive plants.
6.3 Exposure and sensitivity of the Technology to gradual climate change and climate-related extremes/ disasters (as perceived by land users)
Gradual climate change
Gradual climate change
Season | increase or decrease | How does the Technology cope with it? | |
---|---|---|---|
annual temperature | increase | very well | |
seasonal temperature | dry season | increase | very well |
seasonal rainfall | wet/ rainy season | decrease | very well |
Climate-related extremes (disasters)
Meteorological disasters
How does the Technology cope with it? | |
---|---|
local rainstorm | very well |
local sandstorm/ duststorm | very well |
local windstorm | very well |
tornado | well |
Climatological disasters
How does the Technology cope with it? | |
---|---|
drought | very well |
land fire | very well |
Biological disasters
How does the Technology cope with it? | |
---|---|
epidemic diseases | very well |
insect/ worm infestation | very well |
Comments:
The nature of the technology enhances its resilience to disasters and other climatic extremes.
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:
positive
How do the benefits compare with the maintenance/ recurrent costs (from land users' perspective)?
Short-term returns:
positive
Long-term returns:
positive
Comments:
From the perspective of the livestock keepers and the agro-pastoralists, there is no doubt about the economic and financial viability of the firebreaks. They enhance rational management of the available grazing land, by establishing a dynamic of conservation and protection. The costs of implementation and maintenance are much lower than the income generated and received from the DNPGCCA (National Mechanism for the Prevention and Management of Disasters and Food Crises), and especially lower than the opportunity costs (of the grazing land saved from bush fires) in the short/medium and long term.
6.5 Adoption of the Technology
- 1-10%
If available, quantify (no. of households and/ or area covered):
Almost 10% of the livestock keepers in the zone have adopted the technology, focusing on the collection and storage of the straw.
Of all those who have adopted the Technology, how many did so spontaneously, i.e. without receiving any material incentives/ payments?
- 91-100%
Comments:
These livestock keepers have adopted the technology spontaneously on small surfaces. They understood the need to stockpile straw for the lean season.
6.6 Adaptation
Has the Technology been modified recently to adapt to changing conditions?
Yes
If yes, indicate to which changing conditions it was adapted:
- changing markets
Specify adaptation of the Technology (design, material/ species, etc.):
The adaptation consisted of developing markets for the straw, and especially for forage seeds, which are collected during the weeding of the firebreaks. This adaptation led to increased marketing of the straw, and in this way transformed the management of the natural resources. According to the organisations of livestock keepers, like the “Association to Revitalize Livestock keeping in Niger” (AREN), the effect of sale of the straw is negative: it puts an additional pressure on this resource, which cannot effectively recover due to climate change.
6.7 Strengths/ advantages/ opportunities of the Technology
Strengths/ advantages/ opportunities in the land user’s view |
---|
The protection of the grazing land. In this region, where bush fires are common, a significant reduction of the impacts of these fires on the grazing land decreases the vulnerability of the local populations. |
The marketing of the straw. Significant income was generated following the implementation of the firebreaks. |
The ease of implementation and maintenance of the technology, and its low costs, apart from labour. |
Strengths/ advantages/ opportunities in the compiler’s or other key resource person’s view |
---|
The protection of the grazing areas from the impacts of bush fires, which have become a disaster for the transhumant livestock keepers in the last decades. |
The approach of “cash for work”, which was implemented during the construction of the firebreaks, enables on the one hand support of the vulnerable populations during the lean season, and on the other hand the creation of positive momentum for the conservation and protection of the grazing land. The combination of measures for sustainable land management and food security is, without doubt, an effective strategic instrument for this pastoralist zone, which is in an almost chronic state of crisis. |
6.8 Weaknesses/ disadvantages/ risks of the Technology and ways of overcoming them
Weaknesses/ disadvantages/ risks in the land user’s view | How can they be overcome? |
---|---|
The implementation of the technology could threaten the extensive management of the grazing land through the marketing of the straw. | The regulations for the marketing of straw should be strengthened, and especially the rural markets should be regulated. |
The transport of the straw carries along certain forage seeds to other zones, where they could become invasive plants. | An effective transport system for the straw should be put in place. |
Weaknesses/ disadvantages/ risks in the compiler’s or other key resource person’s view | How can they be overcome? |
---|---|
The systematic marketing of the straw is a major weakness. This may reduce the potential of the vegetation cover to regenerate in the grazing areas, and cause conflicts between the traders of straw and the land users (livestock keepers, agro-pastoralists). | Conservation measures for herbaceous species and measures to control soil degradation should be put in place in the firebreaks. |
7. References and links
7.1 Methods/ sources of information
- field visits, field surveys
Two leaders from the NGO ADR regularly collect information on site from the direct beneficiaries (men and women). Based on this information, the wages are paid and the monitoring report is drafted.
- interviews with land users
At the end of every week, interviews are held by the NGO ADR with 100 direct beneficiaries (50 men and 50 women). This is done to check compliance of the work implemented with the financing agreement, and to check the information collected by the leaders from the NGO.
- interviews with SLM specialists/ experts
The implementation of the technology requires a meeting with the departmental directors of Abalak of the divisions environment, livestock keeping and planning. Two specialists in the laying-out of firebreaks also participated actively in the work. Information was gathered from these specialists on compliance with the national standards.
- compilation from reports and other existing documentation
The financing agreement and the reports on the execution, monitoring and evaluation of the project were consulted.
When were the data compiled (in the field)?
09/06/2017
7.2 References to available publications
Title, author, year, ISBN:
Rapport du projet d'ouverture de bandes pare-feux à Ameidida (Abalak, Tahoua)
Available from where? Costs?
NGO ADR, CCA/Prime Minister's Office
7.3 Links to relevant online information
Title/ description:
Les bandes pare-feux du PAAPSSP: une action trois résultats!
URL:
http://www.reca-niger.org/spip.php?article929
Title/ description:
Réflexions: protéger et valoriser les ressources fourragères
URL:
http://www.reca-niger.org/spip.php?article929
Title/ description:
Dispositif National de Prévention et de Gestion des catastrophes et des Crises Alimentaires: un vaste programme de bandes pare-feux
URL:
http://www.dnpgcca.ne/images/Programme%20de%20bandes%20pare%20feu%20-%20Copie.pdf
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