Presented by Azaiez Ouled Belgacem, Mounir Louhaichi and Isabelle Baltenweck at the Euro Tier Middle East 2019 Conference, Abu Dhabi, United Arab Emirates, 2-4 September 2019
VIRUSES structure and classification ppt by Dr.Prince C P
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Opportunities and constraints in pastoral and agro-pastoral livestock systems: The ICARDA/ILRI experience
1. Animal production in
the United Arab
Emirates â Status
and Perspectives
Azaiez Ouled Belgacem1,
Mounir Louhaichi1 and
Isabelle Baltenweck2
Opportunities and constraints in
pastoral and agro-pastoral
livestock systems:
the ICARDA/ILRI experience
Euro Tier Middle East 2019
Conference, Abu Dhabi, United Arab
Emirates, 2-4 September 2019
2. CGIAR on the ground and mandate:
15 research centres; over 70 countries
Reduc
e
povert
y
Impro
ve
food
and
nutriti
on
secur
ity
Improve
natural
resources
and
ecosyste
m
services
3. Agenda 2030âs Sustainable Development Goals
Livestock, including in pastoral systems, contribute to all 17 of
the SDGs and directly to at least 8 of the goals.
4. Opportunities and challenges in the livestock sector
Provides food and nutritional security
BUT overconsumption is often associated with
obesity and non-communicable diseases
Powers economic development
BUT equitable development can be a challenge
Improves human health
BUT animal-human/emerging diseases
and unsafe foods need to be addressed
Enhances the environment
BUT pollution, land/water degradation,
GHG emissions and biodiversity losses
must be greatly reduced
ILRI/Stevie Mann
5. Characteristics of pastoral and agro pastoral
systems
Livestock performs multiple functions:
- Livestock for food, for sale, for prestige, for social functions, as an asset
to store wealth, to protect against shocks
- These systems make use of natural vegetation and other natural
resources
- They play a key role in the protection and maintenance of ecosystems
goods and services
There is a large heterogeneity across systems
- Livestock as the main livelihoods option
- Mixed agro-pastoral systems with integration with cropping
- Off-farm income plays a significant and increasing role in some areas
6. ⢠Climate change (quantity
and quality of food)
⢠Food insecurity and
malnutrition
⢠Natural resources
degradation/depletion
⢠Socio-political instability
⢠Urbanization
⢠Infrastructure/markets
THE CHALLENGES
7. Biradar (2015)
Relative Change in Mean Annual Precipitation
Based on IPCC Scenario A1B, Average of 21 GCMs (1980/99 to 2080/99)
THE CHALLENGES
8. ⢠Higher temperatures
⢠Increase in CO2 concentration
⢠Extreme weather and
unpredictability
⢠Increase frequency of drought
⢠Increase in areas affected by
salinity
⢠Shift in occurrence and
severity of biotic stress
CLIMATE CHANGE â THE MOST LIKELY SCENARIO
THE CHALLENGES
10. 2005 2050
Salsola vermiculata
& Haloxylon
salicornicum in the
Syrian Badia
10
Salsola vermiculata
& Haloxylon
salicornicum in S.
Tunisia
Already threatened rangeland species (such as S. vermiculata) are likely to come under greater danger
and present a very high vulnerability to climate change (blue: absence, red: high abundance)
Vulnerability of rangeland ecosystems to Climate Change
11. Improper grazing practices: Overgrazing and early
grazing
ď Too many animals (high SR)
ď Bad timing: early grazing or prolonged grazing period
The destruction of woody plant species
(uprooting)
ď Medicinal use
ď Fire (energy)
Causes of Rangeland Degradation
12. Causes of Rangeland Degradation
Disruption of the traditional grazing system:
Use of vehicles for transportation of water to the herds and of the animals to
new pastures fosters prolonged grazing on rangelands and uncontrolled
movement of the herds.
13. Causes of Rangeland Degradation
Conversion of the best rangeland sites to cropland
14. Causes/challenges of Pastoral Ecosystems
Degradation in the Drylands
ďLack of policy and weak institutions
ďLand tenure (access & governance)
ďGlobalization (way of life)
Subsidized barley
15. Examples of ILRI-supported innovations: IBLI (index-
based livestock insurance)
ďą Index-Based Livestock Insurance (IBLI): An innovation in insurance
design suitable to the drylands
o Exploiting satellite data on forage availability to design precise and
cheap drought-risk management contracts
o Product designed specifically for pastoralists in the arid and semi-
arid lands
o Satellite imagery is used to assess forage availability and detect
drought related forage scarcity
o Unit areas of insurance takes in account livestock migration patterns
o Compensation provided early in the season to minimize livestock
losses by supporting drought coping strategies
o Product distributed commercially by insurance companies in both
Ethiopia and Kenya with close to 30,000 clients
ďą Sustainable Index-based Livestock Insurance can:
o Prevent downward slide of vulnerable populations
o Allows focus humanitarian resources on the needy
o Crowd-in investment and accumulation by the poor
o Has been adopted by the Government of Kenya as the Kenya
Livestock Insurance programme since 2015 as a social protection
programme covering about 18,000 households
16. Examples of ILRI-supported innovations:
participatory rangeland management (PRM)
⢠Developed to address land and
resource tenure securities and
improve management of these in
a context of reducing authority of
customary institutions.
⢠Piloted in Ethiopia, then scaled-up
with support of NGOs.
⢠Now being piloted in Kenya and
Tanzania .
18. Precipitation (mm)
Grasses Shrubs Trees
Crop diversification
Range/Pasture
based Livestock
farming
Agro-forestry
Mixed farming
Livestock
Pastures
Arable cropping
(Crop diversification)
Agro-forestry
Livestock farming
250 450350
DominantFarmingSystems
Main farming systems in drylands
19. ďRajasthan is the largest
State in India.
ďAbout 55% of the total
area of the State is under
Thar Desert (Great Indian
Desert).
ďMore than 80% of rural
HHs keep animals which
continue to provide
subsistence income during
scarcity.
Facts about Rajasthan state
20. Pastoralists of Rajasthan, India
ď The Raika people represent the majority of the migratory
stock growers in western Rajasthan.
ď For the Raika, domestic animals are living assets
contributing to HH income, food security and health.
ď Their pastoral system, evolved over the last 5 centuries,
and has been centered on the use of large tracts of
uncultivable and marginal land coupled with seasonal
use of rain-fed cropland.
ď Changing demographics, climate, and environmental
awareness is changing their migration patters and land
use.
21. ď Many Raika are very poor and many, especially women,
are illiterate.
ď The migration group generally comes from the same
village.
ď During long distance migration generally 10 to 20 person
move together with their animals for the sake of safety.
ď A respected village leader acts as group leader
(NAMBARDAR). His main task is to finalize the locations
for grazing after talking to different officials/communities
in other locations.
Pastoralists of Rajasthan, India
22. Key issues and challenges
The main constraints faced at the herders
during migration were as follows:
ďShortage of common grazing resources
ď§ Rapid decline of common grazing (quality and
quantity)
ď§ Crop encroachment (cultivation of the best RNG sites)
ď§ Proliferation of invasive species (Prosopis juliflora) in
common lands
ď§ Restrictions to livestock grazing on land controlled by the
forestry department/conservation purposes (parks).
23. ď Institutional support (Services and infrastructure)
ď§ Little or no access to support services (veterinary,
insurance, extension, credit, etc.).
ď§ Lack of infrastructure for processing and production of
value-added livestock products. Dependence on
middlemen for marketing of products.
ď§ Communication gaps between migratory herders and
government officials.
ď Conflicts during migration
ď§ Farmersâ unwillingness to allow grazing on their fallow
lands and harvested fields.
ď§ Theft of animals during residence in other states.
Key issues and challenges
27. Migration from the Home Area begins on 13 February 2013
Migration distance is approximately 550 km in 63 days
Cattle Positions Showing Migration Route
28. Daily Travel DistanceDailyTravelinMeters
Local Date
Migration Begins
Cattle travelled an average of 7.09 km day-1 before migration began,
8.8 km day-1 during migration, and 8.71 km day-1 averaged across
the entire observation period.
29. Migration & Water
ďMigration routes
depend on
availability of water
and pasture land.
ďWater can be from
wells or water
retention basins.
30. 5 km Buffer on Known Watering Points
ď Known water sources along
the migration route were
identified.
ď 5 km buffers were
constructed around each
water source so that areas
with water limitation could be
identified.
ď Cattle traveled approximately
10 km/day.
ď Cattle watered near noon on
most days.
31. ď Improving the condition of the common grazing
lands and religious trust-owned pastures with
community participation could provide better forage
resources that fulfil the nutritional requirements of
migrating animals.
ď Rangeland improvement projects, dissemination of
near real-time information about the condition and
abundance of forage resources and availability of crop
aftermath/fallow fields would facilitate the migration
process and increase efficiencies.
Policy Recommendations
32. Policy Recommendations
ď Institutional support (services & Infrastructure):
ď Creation of livestock watering points on different migratory
routes will help to enhance the productivity.
ď Provision of market infrastructure in production regions to
facilitate sale of animals at remunerative prices.
ď The interventions of state agencies through provision of
mobile veterinary services and quality medicines on
different migratory routes will help reducing losses to
livestock owners.
ď Control of criminals shall provide a healthy space to
livestock owners in different regions and ensure safety of
people engaged in this enterprise.
ď Special program should be in place to look after woman &
children in the absence of male (gender).
34. Revival of traditional grazing
system
Rangeland Himas contributes to poverty
reduction and economic growth as well as
protection of habitat and conservation of
endangered species
35. Advantages
⢠Easy to implement,
⢠Low cost,
⢠Rest technique to improve rangelands productivity
Rest/Deferred Grazing
Southern Tunisia/ Average rainfall: 100 mm
After 2 years rest
36. Impact of resting technique on rangeland
productivity of the communal rangelands of
Chenini, Tunisia (Ouled Belgacem et al., 2008)
Indicators
Free
grazing
Protected
Plant cover (%) 38.7 52.4
Species richness (%) 22 52
Biomass production (kg
DM/ha)
236 2135
Range value (FU/ha) 32 120
50,000 ha of collective rangelands are already under restâŚ
and managed fully by CBOs
37. icarda.org
The option of using local feed resources (shrubs,
promising forages, crop residues, by-products)
ď§ More economic than the use of
concentrates
ď§ More ecological as they integrate
the animal to its environment and
can improve soil and water
conservation
ď§ More sustainable than grain
(cropping or import)
Local Solution
for a Global
Problem
38. There is great scope to reduce areas
under fodder crops by using,
innovating and developing alternate
animal feed resources;
⢠utilizing agricultural and agro-
industrial by-products as feed
blocks, silage and/or mixed with
the ration.
⢠Feed block technology is simple
and does not require sophisticated
equipment.
⢠Blocks are easy to handle, transport
and can be made at the farm levels
using the family labor.
Alternative Feed Resources (valorizing farm by products)
Different formulae with different levels of urea, binders and a wide
range of agro-industrial by-products, which are available locally mainly
date palm by-products are under study in close collaboration between
ICARDA and NARS.
39. icarda.org
ď§ Drought tolerant
ď§ Evergreen habit
ď§ Easy to establish, to maintain & to
use
ď§ Multipurpose use
ď§ Fodder potential
ď§ Resolve livestock watering
ď§ High palatability & high in soluble
carbohydrates
Spineless cactus: a strategic fodder bank for
the arid areas
Biomass production: 40 tons DM/ha
40. Introduction of 38accessionsodspinelesscactus which showedhigh adaptionto the
ArabianPeninsula environment
⢠Sourceofenergy,minerals andvitaminsforanimalfeeding
⢠With relatively very lowwaterrequirement (5000
m3/ha/yearinthe NorthernKSA
⢠the biomass productionexceeds 40Kg/plant/yearandthe
fruitproductionis about30Kg
⢠Source ofdrinkingwaterfor livestock: Consuming300gDry
Matterbysmallruminants coverthe waterrequirements
41. icarda.org
Multipurpose barley
ď§ Green barley grazing (Livestock)
ď§ Grain production (Human, Livestock)
ď§ Straw production (Livestock)
ď§ Stubble grazing (Livestock, Soil
mulch)
43. icarda.org
Sustainable Development of agro-pastoral production systems
Success Factors:
ď§ Multi-stakeholder engagement and
institutional collaborations that leverage
resources and knowledge and improve
overall efficiency of the actions
ď§ Long-term investments by financing
agencies and long-term commitment by
actors
ď§ Favorable and supportive national and
local policy processes
ď§ Use of local practices and knowledge in
the implementation scheme
ď§ Empowerment of the community to own
the process Use of a particular
intervention in the
restoration of degraded
agro-silvopastoral site is
site specific â no one single
rule to apply anywhere!!
44. Challenges:
-Necessity to cover the increasing animal requirements
fromforages
-Cultivation by farmers of high water consuming exotic
forages (Rhodes grass and Alfalfa): about
40000m3/ha/year
Development and introduction of native
less water consuming forages such as
Buffel grass (water requirements less than
15000m3/ha/year
Achievements & Impacts: Enhancing food production and water security
Buffel grass: water saving forage production
Arabian Peninsula (AFESD, IFAD)
45. ⢠Huge water savings in water
scarce countries: switching to
Buffel Grass (Libid) for forage
reduces water requirement by
50%
â Oman growers produce
418,366 tons of Green
Rhodes grass, with 228 million
m3 of water.
â For producing same amount of
forage with Buffel grass, only
116 million m3 of water was
required.
Potential national water savings:
112M m3.
Buffle Grass: high-
nutrition forage crop
with less water
requirements.
46. ďRangelands represent largest land use
ďThey contribute to the living of the poorest
populations (pastoral communities)
ďProvide various ecosystem services and goods
to society
ďResilient system
ď Pastoralists are the most capable to adapt to CC
ďPastoralism is an efficient production system
ď Low input
ď If it is properly executed it sustains healthy
ecosystems
Opportunities
47. o Digital revolution in agriculture (mobile phone, drones, GPS,
remote sensing, sensors, etc.)
⢠Mobile technology
⢠Knowledge exchange
⢠Market integration
⢠Timely access to inputs to follow recommendations
⢠Convergence of multiple actors along the value chain
o Climate change predictions
o Renewed attention to nutrition â livestock essential part of
dietary diversity
o Agribusiness enterprises
o Partnership for synergy and innovation
Opportunities
Hinweis der Redaktion
In addition
Challenge of CC
Recurrent droughts
9
Not specific to a particular region
Natural vegetation[edit]
Prosopis cineraria or Khejri
The natural vegetation of this dry area is classed as Northern Desert Thorn Forest[9] occurring in small clumps scattered more or less openly. Density and size of patches increase from west to east following the increase in rainfall. Natural vegetation of Thar Desert is composed of the following tree, shrub and herb species.[10]
Small trees and shrubs[edit]
Calligonum polygonoides, Acacia jacquemontii, Balanites roxburghii, Ziziphus zizyphus, Ziziphus nummularia, Calotropis procera, Suaeda fruticosa, Crotalaria burhia, Aerva javanica, Clerodendrum multiflorum, Leptadenia pyrotechnica, Lycium barbarum, Grewia tenax, Commiphora mukul, Euphorbia neriifolia, Cordia sinensis, Maytenus emarginata, Capparis decidua, Mimosa hamata
Herbs and grasses[edit]
Ochthochloa compressa, Dactyloctenium scindicum, Cenchrus biflorus, Cenchrus setigerus, Lasiurus scindicus, Cynodon dactylon, Panicum turgidum, Panicum antidotale, Dichanthium annulatum, Sporobolus marginatus, Saccharum spontaneum, Cenchrus ciliaris, Desmostachya bipinnata, Eragrostis species, Ergamopagan species, Phragmites species, Tribulus terrestris, Typha species, Sorghum halepense, Citrullus colocynthis
The Raika Indigenous Peoples of Rajasthan, India
The Raika of Rajasthan, also known as the Rebaris or Dewasis, are an indigenous group of animal breeders and livestock raisers living in northwestern India. Traditionally they lived a semi-nomadic life tied to the arid and semi-arid desert/savanna region on the fringers of the Thar (or Great Indian) Desert. The Raika indigenous people are not an ethnic or linguistic group unto themselves, but rather represent an extensive endogamous caste community. This means that they marry within a larger lineage group and tend toward a common set of occupations. Currently there are an estimated 300,000 Raika living in western Rajasthan and the Marwar region of India.
Anthropologists have documented that the Raika people date back at least 500 or more years, and they are believed to have originated in Persia or Baluchistan. Contemporarily, they are highly regarded for their extensive ecological and veterinary knowledge, as well as for their ability to manage large herds of animals in the harsh Rajasthan environment. This relationship with animals is exhibited in their semi-nomadic lifeway. Historically the Raika kept permanent dwellings in settled villages, which they lived in during various parts of the year. Recently, however, as the result of various pressures they have had to become increasingly nomadic in order to maintain their traditional way of life.
Traditionally the Raika indigenous peoples managed and bred animals, as well as supplied camels, for the maharajas and rajas (kings) of the vast feudal states of the region. In this role, the Raika were strongly identified with the camel and have relied on them for several hundred years. Recently, as modern modes of transportation have penetrated northwestern India, they have had to also incorporate sheep and goats. Presently the Raika combine agricultural production (pearl millet [bajra], wheat [gyon], and arid legumes) and pastoralism (animal breeding and wool products).
In recent years the Raika have thrived, owing to their ability to adapt to radically changing conditions. However, whether the Raika can continue to adapt and maintain their traditional lifeways remains an open question. Currently the threat of closed forests, intensification of agriculture, disintegrating relationships with other groups, state development projects, a quickly changing economy, and invasive plant species are all having an impact on Raika and their indigenous way of life.
The forests of India have historically been held in reserve by the state. In ancient India, forestlands were held by kings for hunting, while in the later colonial British rule they were placed under the control of a government bureaucracy and expert cadre of foresters. After British colonial rule ended, the forests were placed under management of the Ministry of the Environment and are currently managed by state departments of forestry. These forests, for the Raika, are an essential resource for dry-season grazing. However, as these forests become increasingly off-limits for animals or are reserved for conservation purposes, a key foundation stone of their traditional lifeway is removed. In fact, the proliferation of wildlife conservation areas in India has led to an increased tension between the Raika and wildlife officials. For example, the Indian Supreme Court decided that any kind of "resource collection," including grazing of animals in wildlife conservation areas was illegal. This decision effectively cut off over 120,000 hectares in Rajasthan alone that the Raika traditionally relied on for the grazing of their animal herds.
As conservation has removed some dry-season tree pastures for the Raika, so too has the intensification of agriculture and the development of state sponsored projects in the area. Similarly, a decline in the local camel economy has caused the Raika to search out new economic outlets. Finally, the invasion of aggressive foreign plant species has created an ecological crisis and threatened what pasturage remains in the region. Both Mexican mesquite (Prosopis juliflora) and Lantana (Lantana camera) have rendered large areas of traditional pasture useless.
The Raika indigenous people, however, have not faced these transformations passively. Instead, they have organized, adapted, and transformed themselves to meet the challenges they face by involving themselves increasingly in regional and national politics, by modernizing their relationship to the market, and by educating their young. Through these efforts the Raika have continued to maintain their traditional identity and culture, and they are slowly gaining a place within the local and regional politics and economy.