1.2 Detalles de contacto de las personas de referencia e instituciones involucradas en la evaluación y la documentación de la Tecnología

1.3 Condiciones referidas al uso de datos documentados mediante WOCAT

¿Cuándo se compilaron los datos (en el campo)?

26/01/2018

El compilador y la/s persona(s) de referencia claves aceptan las condiciones acerca del uso de los datos documentados mediante WOCAT:

Sí

1.4 Declaración de la sostenibilidad de la Tecnología descrita

¿La Tecnología aquí descrita resulta problemática en relación a la degradación de la tierra, de tal forma que no puede considerársela una tecnología sostenible para el manejo de la tierra?

No

2.1 Breve descripción de la Tecnología

Definición de la Tecnología:

This 'Rangeland Restoration' technology is part of a 'Holistic Rangeland Management' approach. It involves clearing of invasive vegetation (predominantly Acacia reficiens) and reseeding with grass (Cenchrus ciliaris) and allowing resting and reduced grazing pressure to rehabilitate degraded communal grazing land.

2.2 Descripción detallada de la Tecnología

Descripción:

The 'Rangeland Restoration' technology is applied in degraded sites within the 3,100 Ha 'core conservation area' (an central area with minimised grazing pressure designated for tourism) and 'buffer zone' (an area surrounding the 'core conservation area' with reduced grazing pressure) of the Kalama Community Wildlife Conservancy (total area: 9,500 Ha).

The main characteristics are clearing of invasive woody vegetation (predominantly Acacia reficiens) and reseeding with grass (Cenchrus ciliaris). Acacia reficiens (commonly known as red-bark acacia, red thorn or false umbrella tree or thorn) is a native tree or shrub but is considered an invasive species as it can encroach degraded areas with bare and disturbed soil. It is very opportunistic and hardy and can subsequently take over large areas of native vegetation. The invasion can reach a closed or nearly closed canopy with A. reficiens thickets, which are hindering animals to enter and access fodder thus making the area inaccessible for grazing and browsing. Additionally it can be observed that the soil underneath the canopy remains bare and the grass growth seems to be suppressed. As a result the top soil is compacted or forms crusts, which hinder infiltration. During the erratic but heavy rains most of the water flows away as runoff (research in close by areas show that runoff is between 60-80 % of the rainfall) and increases soil erosion and further degradation of the land despite a rather good tree cover. Rangeland grass and fodder productivity in these areas are reduced to a fraction of their potential.
The main activity is the cutting of the trees and shrubs at a height of ~1 m. The main trunks and branches can be used for fencing, temporary house constructions, firewood and charcoal. Most of the cut trees and the remaining branches are used to spread on the bare land where the trees and shrubs are cut. Underneath this dead material the bare soil receives some cover, which creates favorable conditions and microclimate for termites and other fauna in the soil to brake the hard top soil and crust and enable infiltration of the water during the next rains. This allows regrowth of grasses, particularly in the areas protected by the branches. In the following seasons the spread of the grasses can increase also the the area not protected by the branches. Additionally, seeding with Cenchrus ciliaris (buffel-grass or African foxtail grass), a grass species which is native to most of Africa, enhances the growth of a highly valuable fodder grass. Seeds are hand-broadcasted in the treated areas and germinate during the next rainy season. The first greening is visible in the places where the branches and the wood pieces cover the soil. From there the local annual and perennial grasses start colonising and expanding in the following seasons until, ideally, the whole area that has been bare is covered by valuable perennial grasses. Parallel to the cutting and reseeding is reduced grazing pressure and a resting period over at least one dry season, which is facilitated by the fact that treated areas are situated in the core conservation area or in the buffer zone. This involves the cooperation of the members of Kalama Conservancy, who agree to restrict grazing in the buffer zone and more so in the core conservation area. The exact duration that grazing is allowed in each of these two areas varies year to year depending on drought severity and forage availability. Whereas the grazing pressure by livestock can be regulated, there remains uncontrolled grazing by wildlife. The major herbivores are zebra, elephants and a number of different gazelle and antelope species the grazing pressure by wildlife varies but can be substantial at certain times.

Rehabilitating degraded grazing land is the primary purpose of the technology. Other benefits of the technology include: 1) augmented forage availability for the community; 2) increased livestock production; 3) reduced soil erosion and flooding. Land users enjoy these benefits but would like larger areas to be similarly restored. However, the limiting factor is the funding required to pay for labour, which is the major input required for the clearing and reseeding activities. Establishing a market for removing the main stems and producing and selling charcoal is still an opportunity to further explore immediate benefits and cash income in order to pay for the investment into the clearing.

2.3 Fotografías de la Tecnología

2.5 País/ región/ lugares donde la Tecnología fue aplicada y que se hallan comprendidos por esta evaluación

2.6 Fecha de la implementación

Indique año de implementación:

2006

Si no se conoce el año preciso, indique la fecha aproximada:

• 10-50 años atrás

2.7 Introducción de la Tecnología

Especifique cómo se introdujo la Tecnología:

• mediante proyectos/ intervenciones externas

Comentarios (tipo de proyecto, etc.):

Acacia reficiens was already selectively cleared traditionally when constructing livestock corrals ('bomas'), but the introduction of more extensive clearing and grass-reseeding to rehabilitate specific areas was facilitated by Northern Rangeland Trust and Grevy's Zebra Trust.

3.1 Propósito(s) principal(es) de la Tecnología MST

• reducir, prevenir, restaurar la degradación del suelo
• conservar el ecosistema
• preservar/ mejorar biodiversidad

3.2 Tipo(s) actuales de uso de la tierra donde se aplica la Tecnología

3.3 Información adicional sobre el uso de tierras

Provisión de agua para la tierra donde se aplica la Tecnología:

• de secano

Número de temporadas de cultivo por año:

• 2

Especifique:

Rainiy seasons from April to June and from October to December but with high variability in time and amount

Densidad del ganado (si fuese relevante):

likely continuously growing till technology was introduced

3.4 Grupo MST al que pertenece la Tecnología

• pastoralismo y manejo de tierras de pastoreo
• cobertura de suelo/ vegetal mejorada
• variedades vegetales/ razas animales mejoradas

3.5 Difusión de la Tecnología

Especifique la difusión de la Tecnología:

• aplicada en puntos específicos/ concentrada en un área pequeña

3.6 Medidas MST que componen la Tecnología

3.7 Principales tipos de degradación del suelo encarados con la Tecnología

3.8 Prevención, reducción o restauración de la degradación del suelo

Especifique la meta de la Tecnología con relación a la degradación de la tierra:

• reducir la degradación del suelo
• restaurar/ rehabilitar tierra severamente degradada

4.1 Dibujo técnico de la Tecnología

4.2 Especificaciones técnicas/ explicaciones del dibujo técnico

A total of 279 hectares were treated with this rangeland restoration technology (clearing invasive Acacia reficiens and reseeding with Cenchrus ciliaris). Treated areas were relatively flat (slope < 5%). A. reficiens were cut ~1 m above the ground and well before the onset of the rains to discourage regeneration. C. ciliaris seeds were hand-broadcast at a rate of ~45 kg/Ha.
Holding membership of multiple community conservancies facilitates the movement between wet season and dry season grazing areas. For example, many of the local communities move their livestock to Losesia, in Sera Conservancy, for dry season grazing. These porous boundaries relieve pressure from Kalama Conservancy during some parts of the year, potentially facilitating recovery of treated areas, but also allows neighbouring communities to access treated areas rendering their grazing management challenging.

4.3 Información general sobre el cálculo de insumos y costos

Especifique cómo se calcularon los costos e insumos:

• por área de Tecnología

otra / moneda nacional (especifique):

Kenya Shillings

Indique la tasa de cambio de USD a la moneda local (si fuese relevante): 1 USD =:

101,0

4.4 Actividades de establecimiento

	Actividad	Tipo de medida	Momento
1.	Clearing Acacia reficiens (cutting and spreading)	Vegetativas	During dry season, well before the onset of rains to prevent Acacia reficiens regrowth from stump.
2.	Reseeding with Cenchrus ciliaris grass seed	Vegetativas	Prior to the onset of rainy season to maximise germination and establishment of Cenhrus ciliaris..

4.5 Costos e insumos necesarios para el establecimiento

	Especifique insumo	Unidad	Cantidad	Costos por unidad	Costos totales por insumo	% de los costos cubiertos por los usuarios de las tierras
Mano de obra	Clearing Acacia reficiens	person-days	1200,0	450,0	540000,0
Mano de obra	Hand-broadcasting Cenchrus ciliaris seeds	person-days	1200,0	450,0	540000,0
Equipo	Machettes	units	40,0	500,0	20000,0
Material para plantas	Cenchrus ciliaris seeds	kg	2520,0	50,0	126000,0
Otros	Transport of workers to and from site	litre	600,0	100,0	60000,0
Costos totales para establecer la Tecnología					1286000,0

Si el usuario de la tierra no cubrió el 100% de los costos, indique quién financió el resto del costo:

Funding raised by Northern Rangelands Trust and Grezy's Zebra Trust (including USAID and FAO funding).

Comentarios:

These are the costs associated a 55 Ha treated area. Six sites of a similar size were treated with similar budgets totalling 279 Ha.

4.6 Actividades de establecimiento/ recurrentes

Comentarios:

No maintenance activities.

4.7 Costos e insumos necesarios para actividades de mantenimiento/ recurrentes (por año)

Comentarios:

No maintenance costs.

4.8 Factores más determinantes que afectan los costos:

Describa los factores más determinantes que afectan los costos:

Hiring labour, as it was the most costly component.

5.1 Clima

5.2 Topografía

Indique si la Tecnología se aplica específicamente en:

• no relevante

5.3 Suelos

Si se halla disponible, adjunte una descripción completa de los suelos o especifique la información disponible, por ej., tipo de suelo, pH/ acidez de suelo, capacidad de intercambio catiónico, nitrógeno, salinidad, etc. :

pH ~7-8.5; SOC 4.7 g/kg of soil; Na ~0.1-0.4 cmolc/kg

5.4 Disponibilidad y calidad de agua

¿La salinidad del agua es un problema?

No

¿Se está llevando a cabo la inundación del área? :

No

5.5 Biodiversidad

Comentarios y especificaciones adicionales sobre biodiversidad:

Rangelands in Kenya are generally characterized by high bio-diversity. The particular sites have been degraded in terms of vegetation ans soils. After the restoration diversity increases but has not reached its full potential.

5.6 Las características de los usuarios de la tierra que aplican la Tecnología

Indique otras características relevantes de los usuarios de las tierras:

Kalama Conservancy receives considerable income from the high end tourism (~60% of total income) and donations (~25% of total income).

5.7 Área promedio de la tierra que pertenece a o es arrendada por usuarios de tierra que aplican la Tecnología

5.8 Tenencia de tierra, uso de tierra y derechos de uso de agua

Tenencia de tierra:

• comunitaria/ aldea

Derechos de uso de tierra:

• comunitarios (organizado)

Derechos de uso de agua:

• comunitarios (organizado)

5.9 Acceso a servicios e infraestructura

6.1 Impactos in situ demostrados por la Tecnología

Impactos socioeconómicos

Producción

Impactos socioculturales

Impactos ecológicos

Ciclo de agua/ escurrimiento de sedimento

Suelo

Biodiversidad: vegetación, animales

6.2 Impactos fuera del sitio demostrados por la Tecnología

6.3 Exposición y sensibilidad de la Tecnología al cambio climático gradual y a extremos relacionados al clima/ desastres (desde la percepción de los usuarios de tierras)

Cambio climático gradual

Cambio climático gradual

	Estación	tipo de cambios climáticos/ climas extremos	¿Cómo es que la tecnología soporta esto?
temperatura anual		incrementó	moderadamente

Extremos (desastres) relacionados al clima

Desastres climatológicos:

	¿Cómo es que la tecnología soporta esto?
tormenta de lluvia local	muy bien

Desastres climatológicos

	¿Cómo es que la tecnología soporta esto?
sequía	bien

6.4 Análisis costo-beneficio

¿Cómo se comparan los beneficios con los costos de establecimiento (desde la perspectiva de los usuarios de tierra)?

6.5 Adopción de la Tecnología

• casos individuales / experimentales

De todos quienes adoptaron la Tecnología, ¿cuántos lo hicieron espontáneamente, es decir, sin recibir incentivos/ pagos materiales?

• 0-10%

6.6 Adaptación

¿La tecnología fue modificada recientemente para adaptarse a las condiciones cambiantes?

No

6.7 Fuerzas/ ventajas/ oportunidades de la Tecnología

Fuerzas/ ventajas/ oportunidades desde la perspectiva del usuario de la tierra
Land that was previously considered unproductive is now considered grazing land.
Increased infiltration and decreased runoff and water erosion.
Recolonisation by local grasses and forbs to replace reseeded Cenchrus ciliaris after 1-2 years provides nutritious forage (particularly the forbs) for livestock.

Fuerzas/ ventajas/ oportunidades desde la perspectiva del compilador o de otra persona de referencia clave
Decreased impact of the invasive Acacia reficiens on vegetation and soil within treated areas.
Increased biomass of herbaceous vegetation for livestock and wildlife forage.
Augmented biodiversity after reseeded Cenchrus ciliaris replaced by local grasses and forbs.

6.8 Debilidades/ desventajas/ riesgos de la Tecnología y formas de sobreponerse a ellos

Debilidades/ desventajas/ riesgos desde la perspectiva del usuario de la tierra	¿Cómo sobreponerse a ellas?
Creates overly high expectations from the community regarding the potential to restore larger areas.	Raise awareness among community members regarding the limitations of large-scale restoration.
Lack of funds to pay labourers. Paying community members to undertake restoration activities rather than these activities being voluntary is now, in hindsight, perceived to have been a mistake.	There will never be enough funding as labourers will continue to expect ever-increasing wages. However, over time, community members may decide to restore land voluntarily. Explore the potential for marketing the main trunks for charcoal production of firewood to pay for the labourers.
Controlling grazing in recovering areas.	Raise awareness about the restoration projects within immediate and neighbouring communities. Also, ensure grazing by-laws are implemented and offenders fined.
Land users unwilling to voluntarily take part in restoration activities.	Increase ownership by conducting restoration projects at more local zonal-levels rather than at the conservancy-level. Create additional incentives by using and marketing of some of the wood material (for legal charcoal production)

Debilidades/ desventajas/ riesgos desde la perspectiva del compilador o de otra persona de referencia clave	¿Cómo sobreponerse a ellas?
Inability to provide adequate rest to treated areas (i.e. by controlling grazing pressure) leading to unsuccessful establishment of Cenchrus ciliaris or other herbaceous vegetation in treated areas, particularly in 'buffer zone'.	Implement grazing rules more stringently.
Lack of capacity regarding how to reseed Cenchrus ciliaris in some treated areas. In one case, seeds were buried (as farmers do with maize seeds), which is reported to have contributed to low establishment success of C. ciliaris seeds.	Capacity building.
Germination and establishment of Cenchrus ciliaris depends on timing in relation to the onset of rains, which are unpredictable and led to unsuccessful rehabilitation of some treated areas.	Provide most accurate weather forecasts available.

7.1 Métodos/ fuentes de información

7.2 Vínculos a las publicaciones disponibles

Título, autor, año, ISBN:

'Northern Rangeland Trust: Baseline assessment of rangeland health - Kalama and Namunyak conservancies', Tor-G. Vågen & Leigh A. Winowiecki, 2014

¿Dónde se halla disponible? ¿Costo?

https://cgspace.cgiar.org/bitstream/handle/10568/65671/nrtReport_march2014.pdf?sequence=1

7.3 Vínculos a la información relevante disponible en línea

Título/ descripción:

Northern Rangeland Trust: Baseline assessment of rangeland health - Kalama and Namunyak conservancies

URL:

https://cgspace.cgiar.org/bitstream/handle/10568/65671/nrtReport_march2014.pdf?sequence=1