Gully control and catchment protection [Bolivie]
- Création :
- Mise à jour :
- Compilateur : Georg Heim
- Rédacteur : –
- Examinateur : Fabian Ottiger
Control de cárcavas (spanish)
technologies_1350 - Bolivie
Voir les sections
Développer tout Réduire tout1. Informations générales
1.2 Coordonnées des personnes-ressources et des institutions impliquées dans l'évaluation et la documentation de la Technologie
Spécialiste GDT:
Vargas Ivan
Cochabamba
Bolivie
Nom du projet qui a facilité la documentation/ l'évaluation de la Technologie (si pertinent)
Book project: where the land is greener - Case Studies and Analysis of Soil and Water Conservation Initiatives Worldwide (where the land is greener)Nom du ou des institutions qui ont facilité la documentation/ l'évaluation de la Technologie (si pertinent)
GEOTEST AG (GEOTEST AG) - Suisse1.3 Conditions relatives à l'utilisation par WOCAT des données documentées
Quand les données ont-elles été compilées (sur le terrain)?
01/09/2003
Le compilateur et la(les) personne(s) ressource(s) acceptent les conditions relatives à l'utilisation par WOCAT des données documentées:
Oui
1.5 Référence au(x) questionnaire(s) sur les Approches de GDT
Incentive-based catchment treatment [Bolivie]
A project supported, incentive-based approach: farmers are sensitised about erosion, and involved in gully control and other measures to protect catchments.
- Compilateur : Unknown User
2. Description de la Technologie de GDT
2.1 Courte description de la Technologie
Définition de la Technologie:
Integrated gully treatment consisting of several simple practices including stone and wooden check dams, cut-off drains and reforestation in sediment traps (biotrampas).
2.2 Description détaillée de la Technologie
Description:
The focus of the case study is a degraded catchment, located at high altitude (2,800–4,200 m a.s.l.), home to 37 households, which is characterised by severe gullies and landslides. Gullies are continuously expanding, and constitute a significant proportion of the catchment. These cause considerable loss of cropland as well as downstream damage to the city of Cochabamba.
A combination of structural and vegetative measures was designed and implemented with the purpose of: (1) preventing affected areas from further degradation by safely discharging runoff from the surrounding area through the main gullies down to the valley; (2) gradually stabilising the land through the regeneration of vegetative cover; (3) reducing downstream damage through floods and siltation; (4) ensuring accessibility to the mountainous agricultural area during the rainy season.
Cut-off drains at the heads of the gullies, reinforced with stones inside the channel and grassed bunds below, concentrate runoff and cascade it down over stone steps back into the waterways. Flow is controlled by stone and wooden check dams and discharged safely. Sediment is trapped behind these structures and terraces develop. Bushes or trees are planted above and below the check dams. Depending on availability of materials, wooden check dams are sometimes used and associated with tree planting (four trees above and four below each check dam).
These practices are complemented by SWC measures throughout the catchment: biotrampas are staggered sediment traps located on the steep lateral slopes. They comprise ditches behind wooden barriers where soil accumulates. Biotrampas create suitable sites for tree/bush planting while stabilising the hillsides, reducing erosion, increasing infiltration and slowing siltation of the check dams in the watercourses. Supporting technologies include fenced-off areas for reforestation of the lateral slopes/upper edge of the gully, and finally large gabion dams at the outlets of the gullies, usually 10-25 m in length, but exceptionally up to 200 m.
After a few years vegetation should have stabilised the system, and effectively replaced the wooden and stone constructions. The various practices enhance each other. Establishment is labour demanding, but other costs are low, as long as the material in question is locally obtainable. Maintenance costs are also low. The technology was implemented over a period of six years, starting in 1996, through the Programa de Manejo Integral de Cuencas (PROMIC).
2.3 Photos de la Technologie
2.5 Pays/ région/ lieux où la Technologie a été appliquée et qui sont couverts par cette évaluation
Pays:
Bolivie
Région/ Etat/ Province:
Cochabamba District,
Autres spécifications du lieu:
Pajcha Watershed Cordillera del Tunari
Map
×2.7 Introduction de la Technologie
Spécifiez comment la Technologie a été introduite: :
- par le biais de projets/ d'interventions extérieures
3. Classification de la Technologie de GDT
3.1 Principal(aux) objectif(s) de la Technologie
- réduire, prévenir, restaurer les terres dégradées
3.2 Type(s) actuel(s) d'utilisation des terres, là où la Technologie est appliquée
Terres cultivées
- Cultures annuelles
Pâturages
Commentaires:
Major land use problems (compiler’s opinion): Deforestation, overgrazing and poorly managed channel irrigation in areas with steep slopes: poorly structured soils and
extreme climatic variability causing erosion gullies, landslides, downstream flooding and sedimentation of agricultural land and settlements - including the city of Cochabamba.
Other grazingland: extensive grazing
3.3 Informations complémentaires sur l'utilisation des terres
Approvisionnement en eau des terres sur lesquelles est appliquée la Technologie:
- pluvial
Précisez:
Longest growing period in days: 210 Longest growing period from month to month: Oct - Apr
3.4 Groupe de GDT auquel appartient la Technologie
- mesures en travers de la pente
- dérivation et drainage de l'eau
- Sediment traps
3.5 Diffusion de la Technologie
Commentaires:
Total area covered by the SLM Technology is 6 m2.
3.6 Mesures de GDT constituant la Technologie
3.7 Principaux types de dégradation des terres traités par la Technologie
érosion hydrique des sols
- Wg: ravinement/ érosion en ravines
- Wm: mouvements de masse/ glissements de terrain
- Wo: effets hors-site de la dégradation
dégradation biologique
- Bq: baisse de la quantité/ biomasse
Commentaires:
Main type of degradation addressed: Wg: gully erosion / gullying, Wm: mass movements / landslides, Wo: offsite degradation effects, Bq: quantity / biomass decline
3.8 Prévention, réduction de la dégradation ou réhabilitation des terres dégradées
Spécifiez l'objectif de la Technologie au regard de la dégradation des terres:
- restaurer/ réhabiliter des terres sévèrement dégradées
4. Spécifications techniques, activités, intrants et coûts de mise en œuvre
4.1 Dessin technique de la Technologie
4.2 Spécification/ explications techniques du dessin technique
Gully control and catchment protection: an overview of the integrated measures.
Technical knowledge required for field staff / advisors: moderate
Technical knowledge required for land users: moderate
Main technical functions: reduction of slope angle, reduction of slope length, improvement of ground cover, increase in organic matter, sediment retention / trapping, sediment harvesting, control of concentrated runoff
Secondary technical functions: increase of infiltration, control of dispersed runoff
Vegetative measure: grassed bunds
Vegetative material: G : grass
Vegetative measure: aligned trees
Vegetative material: G : grass
Vegetative measure: Vegetative material: G : grass
Vegetative measure: Vegetative material: G : grass
Structural measure: cut-off drains
4.4 Activités de mise en place/ d'établissement
Activité | Type de mesures | Calendrier | |
---|---|---|---|
1. | Plant local bushes and trees in front and behind the biotrampas andthe check dams (after sedimentation). Altitude acclimatisation (2 weeks)is required for the trees before planting. | Végétale | |
2. | Cut-off drains: excavate channel above the gully. Lay stones in the bedand plant local bushes or grass on the bund below the ditch. The outletof the ditch into the gully is stabilised by a few stone steps. | Structurel | |
3. | Stone check dams: excavate a ditch perpendicular to the water channel | Structurel | during the dry season |
4. | Wooden check dams (up to 8 m long, 15–20 cm wide and 1 m high):soil excavation (see 2.). Fix logs with wire or nails to vertical poles.Position a bio-fibre fleece behind the dam to prevent sediment fromflowing through. | Structurel | |
5. | Biotrampas: excavate soil, hammer wooden posts into the soil andfix 2–3 horizontal logs with nails or wire to the wooden posts. | Structurel | (During dry season) |
6. | Plant local bushes and trees in front and behind the biotrampas andthe check dams (after sedimentation). Altitude acclimatisation (2 weeks)is required for the trees before planting. Establish fences to protect the plants. | Structurel |
4.5 Coûts et intrants nécessaires à la mise en place
Spécifiez les intrants | Unité | Quantité | Coûts par unité | Coût total par intrant | % des coût supporté par les exploitants des terres | |
---|---|---|---|---|---|---|
Main d'œuvre | Labour | ha | 1,0 | 48,0 | 48,0 | |
Equipements | Tools | ha | 1,0 | 4,0 | 4,0 | |
Matériel végétal | Seedlings | ha | 1,0 | 19,0 | 19,0 | |
Matériaux de construction | Stone | ha | 1,0 | |||
Matériaux de construction | Wood | ha | 1,0 | 33,0 | 33,0 | |
Matériaux de construction | Nails, wire | ha | 1,0 | 2,0 | 2,0 | |
Matériaux de construction | Bio-fibre fleece | ha | 1,0 | 4,0 | 4,0 | |
Coût total de mise en place de la Technologie | 110,0 |
4.6 Activités d'entretien/ récurrentes
Activité | Type de mesures | Calendrier/ fréquence | |
---|---|---|---|
1. | Biotrampas: pruning the trees | Végétale | /every three years. |
2. | Cut-off drains: clearing of sediment, cutting bushes and grasses. | Végétale | |
3. | Stone check dams: pruning trees and bushes. After full sedimentation, the dam may be increased in height. | Végétale | /every three years. |
4. | Wooden check dams: pruning trees and bushes | Végétale | /every three years |
4.7 Coûts et intrants nécessaires aux activités d'entretien/ récurrentes (par an)
Spécifiez les intrants | Unité | Quantité | Coûts par unité | Coût total par intrant | % des coût supporté par les exploitants des terres | |
---|---|---|---|---|---|---|
Main d'œuvre | Labour | ha | 1,0 | 12,0 | 12,0 | 100,0 |
Equipements | Tools | ha | 1,0 | 1,0 | 1,0 | 100,0 |
Matériel végétal | Seedlings | ha | 1,0 | 1,0 | 1,0 | 100,0 |
Matériaux de construction | Stone | ha | 1,0 | |||
Matériaux de construction | Wood | ha | 1,0 | 1,0 | 1,0 | 100,0 |
Matériaux de construction | Nails, wire | ha | 1,0 | 1,0 | 1,0 | 100,0 |
Coût total d'entretien de la Technologie | 16,0 |
Commentaires:
Costs have been calculated for the whole catchment (6 km2) – including 100 m of cut-off drains, 6,750 m of stone
check dams, 1,500 m of wooden check dams and 770 biotrampas – and then divided by the number of hectares. Wood is not locally available (because of national park laws) and needs to be brought into the area. Establishment and maintenance costs were paid by PROMIC during their intervention period of 6 years. The (high) costs of the gabion weirs further downstream are not included as these are not always required and vary considerably in size from site to site.
5. Environnement naturel et humain
5.1 Climat
Précipitations annuelles
- < 250 mm
- 251-500 mm
- 501-750 mm
- 751-1000 mm
- 1001-1500 mm
- 1501-2000 mm
- 2001-3000 mm
- 3001-4000 mm
- > 4000 mm
Zone agro-climatique
- subhumide
- semi-aride
5.2 Topographie
Pentes moyennes:
- plat (0-2 %)
- faible (3-5%)
- modéré (6-10%)
- onduleux (11-15%)
- vallonné (16-30%)
- raide (31-60%)
- très raide (>60%)
Reliefs:
- plateaux/ plaines
- crêtes
- flancs/ pentes de montagne
- flancs/ pentes de colline
- piémonts/ glacis (bas de pente)
- fonds de vallée/bas-fonds
Zones altitudinales:
- 0-100 m
- 101-500 m
- 501-1000 m
- 1001-1500 m
- 1501-2000 m
- 2001-2500 m
- 2501-3000 m
- 3001-4000 m
- > 4000 m
Commentaires et précisions supplémentaires sur la topographie:
Slopes on average: Also very steep and hilly (both ranked 2) and moderate and rolling (both ranked 3)
5.3 Sols
Profondeur moyenne du sol:
- très superficiel (0-20 cm)
- superficiel (21-50 cm)
- modérément profond (51-80 cm)
- profond (81-120 cm)
- très profond (>120 cm)
Texture du sol (de la couche arable):
- moyen (limoneux)
Matière organique de la couche arable:
- abondant (>3%)
- faible (<1%)
Si disponible, joignez une description complète du sol ou précisez les informations disponibles, par ex., type de sol, pH/ acidité du sol, capacité d'échange cationique, azote, salinité, etc.
Soil depth on average: Also Very shallow (ranked 2) and shallow as well as deep (both ranked 3)
Soil fertility: Low and very low
Topsoil organic matter: High (on the cropland at high altitudes) and low (in the gullies)
Soil drainage/infiltration: Medium
5.6 Caractéristiques des exploitants des terres appliquant la Technologie
Orientation du système de production:
- subsistance (auto-approvisionnement)
Revenus hors exploitation:
- 10-50% de tous les revenus
Indiquez toute autre caractéristique pertinente des exploitants des terres:
Market orientation: Subsistence (mostly subsistence (self-supply) with low market income)
5.7 Superficie moyenne des terres détenues ou louées par les exploitants appliquant la Technologie
- < 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 Propriété foncière, droits d’utilisation des terres et de l'eau
Propriété foncière:
- individu, avec titre de propriété
- communal grassland
Droits d’utilisation des terres:
- communautaire (organisé)
- individuel
6. Impacts et conclusions
6.1 Impacts sur site que la Technologie a montrés
Impacts socio-économiques
Production
production agricole
Commentaires/ spécifiez:
Maintained: Due to prevention of further land loss
production fourragère
Commentaires/ spécifiez:
Maintained: Due to prevention of further land loss
Revenus et coûts
charge de travail
Commentaires/ spécifiez:
High labour input for establishment (though paid in this instance)
Impacts socioculturels
institutions communautaires
connaissances sur la GDT/ dégradation des terres
Impacts écologiques
Sols
humidité du sol
couverture du sol
perte en sol
6.2 Impacts hors site que la Technologie a montrés
inondations en aval
envasement en aval
Benefit not for implementing farmers
Commentaires/ spécifiez:
farmers implementing SWC are not those benefiting most from the impact in the short term
6.4 Analyse coûts-bénéfices
Quels sont les bénéfices comparativement aux coûts de mise en place (du point de vue des exploitants des terres)?
Rentabilité à court terme:
très positive
Rentabilité à long terme:
très positive
Quels sont les bénéfices comparativement aux coûts d'entretien récurrents (du point de vue des exploitants des terres)?
Rentabilité à court terme:
très positive
Rentabilité à long terme:
très positive
6.5 Adoption de la Technologie
Parmi tous ceux qui ont adopté la Technologie, combien d'entre eux l'ont fait spontanément, à savoir sans recevoir aucune incitation matérielle ou aucun paiement?
- 0-10%
Commentaires:
100% of land user families have adopted the Technology with external material support
There is no trend towards spontaneous adoption of the Technology
Comments on adoption trend: Only a few farmers have built new structures post-project. This is due to different reasons: (1) PROMIC stopped its financial support; (2) the gullied areas are not used by farmers, therefore they have little reason to protect them; (3) the catchment is w
6.7 Points forts/ avantages/ possibilités de la Technologie
Points forts/ avantages/ possibilités du point de vue du compilateur ou d'une autre personne ressource clé |
---|
Reduction of landslips and flooding in the valley How can they be sustained / enhanced? New small gullies may originate inside an existing gully or around it. It is important to continue to maintain the current measures and construct new, even though the subsidies of PROMIC have been terminated. |
The technology could be implemented by the farmers themselves as materials (except for wood) and tools are locally available How can they be sustained / enhanced? Prolong the sensitisation work to convince the farmers of the necessity and benefits of the technology. |
Reduction of soil loss in the watershed How can they be sustained / enhanced? Do not apply the mentioned practices in isolation but always in combination. |
Simple technology with high positive long-term impact, especially downstream. |
6.8 Faiblesses/ inconvénients/ risques de la Technologie et moyens de les surmonter
Faiblesses/ inconvénients/ risques du point de vue du compilateur ou d'une autre personne ressource clé | Comment peuvent-ils être surmontés? |
---|---|
The technology doesn’t address the root cause of human induced gully erosion | Alongside the gully control technology it is necessary to apply complementary conservation measures on the cropland above the gully to prevent new gully development. |
High labour input for establishment of SWC measures. | An agreement on sustainable use of trees should be made with the national park authority. |
The technology partly depends on inputs that are not available locally: timber for establishment of wooden structures (which is a significant quantity) are brought in from outside (since the area is within a national park tree felling is not allowed) |
7. Références et liens
7.2 Références des publications disponibles
Titre, auteur, année, ISBN:
Documentation of PROMIC (see address above)
Disponible à partir d'où? Coût?
PROMIC, Programa de Manejo Integral
de Cuencas, Av. Atahuallpa final, Parque Tunari, casilla 4909, Cochabamba, Bolivia; promic@promic-bolivia.org; www.promic-bolivia.org
Liens et modules
Développer tout Réduire toutLiens
Incentive-based catchment treatment [Bolivie]
A project supported, incentive-based approach: farmers are sensitised about erosion, and involved in gully control and other measures to protect catchments.
- Compilateur : Unknown User
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