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Perspectives on Rangeland Development: by
Abstract
FAO
as a technical agency has been involved in working with donors and governments
in the implementation of rangeland development assistance projects for
many years. The key question for FAO is how to eradicate poverty and hunger
and ensure food security and sustainable use of rangeland resources in
the face of increasing human and animal populations?
FAO
emphasises multidisciplinary approaches to range development, through:
people's participation; the importance of local institutions and community
regulatory mechanisms; policies that foster sustainable range development;
the need to consider the often close relationship between pastoral and
agricultural development; the role of Governments in ensuring that appropriate
land tenure regulations are in place; the need to consider alternative
income generating activities; risk management; and aspects such as desertification
and the loss of biodiversity. The focus of this paper is on selected projects
which illustrate the variety of factors involved in rangeland development
Lessons learned and general conclusions are drawn from four case studies
dealing with (a) range rehabilitation, wildlife re-introduction and a participatory
approach to range management on the Syrian steppe, (b) Kazak herders, winter
feed and transhumant systems in Altai Prefecture, Xinjiang, China, (c)
pastoral risk management in Mongolia, and (d) rural development at N’Nguigmi
in Niger.
Keywords:
rangelands FAO experience
Introduction
In
the past, large rangeland development projects have commonly addressed
issues such as: borehole provision, veterinary care, subsidized feeds and
livestock production, revegetation of depleted ranges, feed reserves, establishment
of fodder shrubs, creation of pastoral and fattening co-operatives, establishment
of regulations to optimize utilization of rangeland resources and sedentarizing
of nomads (El-Shorbagy, 1998). However, often projects were hastily implemented
with little consideration of the views or involvement of the local population.
Any failure was blamed on the reluctance of pastoralists to take up the
proposed techniques or ideas, problems of land tenure, the inadequacies
of administrations etc. El-Shorbagy (1998) suggested that rarely has failure
been pinned at the door of the project formulators who failed to consult
the target audience (the pastoralists, the herders, the nomadic peoples)
and failed to understand their needs and expectations. It is important
to understand the role of local institutions and community regulatory mechanisms
(Zaroug, 1995), and there is a need to ensure where possible that mobility
is retained in pastoral systems (UNSO, 1994).
According
to de Haan (1995), livestock and rangeland development projects have had
such a poor success rate that there was reduced overall donor support in
the 1980s. Fortunately, there has been renewed donor interest in the 1990s
(Pratt et al. 1997) and particularly because of the new paradigms
of thinking in range ecology (Behnke and Scoones, 1992; Behnke et al.,
1993; Scoones, 1995, UNSO, 1994).
FAO
Approaches to Rangeland Development
FAO
as a technical agency has been involved in working with donors and Governments
in the implementation of rangeland development assistance projects for
many years. The key questions for FAO were and are: How to eradicate poverty
and hunger and ensure sustainable use of rangeland resources in the face
of increasing human and animal populations? How to ensure food security?
How to maintain systems for future generations?
FAO now emphasises multidisciplinary approaches to range development, including: people's participation; the importance of local institutions and community regulatory mechanisms; policies which will foster sustainable range development; the need to consider the often close relationship between pastoral and agricultural development; the role of governments in ensuring that appropriate land tenure regulations are in place; the need to consider alternative income generating activities; risk management; and aspects such as desertification and the loss of biodiversity. Rather than attempting to review the many projects which have been implemented, some successfully but others less so, the focus of this paper is on the impact and lessons learned from a small number of selected projects which serve to illustrate the variety of factors involved in rangeland development (for a review of projects implemented in the Near East region refer to Zaroug (1995), see also FAO (1995)).
Case
Studies Case
Study 1 - Range rehabilitation, wildlife re-introduction and a participatory
approach to range management in the Syrian steppe In Syria, as in a number of Near East countries where the land is State-owned, there has been a breakdown of traditional systems of management such as the Hema system. Rising population and livestock numbers, and a high degree of mechanisation, have increased pressure on the range and resulted in a severe deterioration of large areas of the Al-Badia rangelands.This project is attempting to demonstrate techniques for improved range production, re-introduce wildlife, and to (re-) establish sustainable range management systems based on an approach of extensive community participation. The
context The Syrian Al-Badia Steppe, climatically characterised by low and erratic rainfall (less than 200 mm per year), cold winters (often below 0 o C) and hot summers (exceeding 45 o C), comprises more than 55% of the land area of Syria or some 10.2 M ha. In spite of the harsh conditions, the Badia remains an important area for livestock raising (Mirreh, 1999). Current range sheep production is highly mechanised through the extensive use of water tankers, trucks and tractors. Programmes for better veterinary care, more watering points and feed subsidies contribute to keeping livestock raising in the Badia an economically attractive business for herders as well as for merchants who have purchased large flocks and put them onto the steppe with sheep herders. However, this type of over-utilization of the rangeland resource has caused considerable deterioration of both soil and vegetation. Uprooting of perennial plants for fuel, combined with the availability of vehicles, has resulted in the clearing of bush cover from large areas (it has been estimated, for instance, that an average Bedouin household annually uses shrubs for fuel from approximately 4.4 ha.). Erosion pavements with limited infiltration and large active gullies are common and there has been a decrease in the numbers of the preferred forage plants such as Salsola vermiculata, Poa sinaica, Plantago albans, Stipagrostis and even Artemisia herba alba which are often replaced by plants of lower forage value such as Peganum harmala, Noa mucronata and Anabasis syriaca (Mirreh, 1999). The
project A
project for the rehabilitation of marginal lands and the establishment
of a wildlife reserve was started in February 1996, attempting
to heal part of the severely degradedAl
Badia steppe. It covers some 130,000 ha including 22,000 ha of wildlife
reserve and 108,000 ha of land from three co-operatives with 426 households
and 3,050 people owning 95,000 head of sheep.Activities
undertaken to date have included direct seeding and shrub planting on 5,000
ha, closing off areas to livestock grazing (3,000 ha),data
collection and monitoring, the preparation of range management plans, assessment
of alternative energy sources for cooking and heating and income generating
activities. In addition, gazelle and oryx have been re-introduced to a
newly created reserve and management plans developed.Major
emphasis is also given to training and capacity building among the national
staff, and to the full involvement of the local communities in range management
planning and implementation. The
project is facing a difficult situation due to a severe drought, which
resulted in the Government deciding to open all protected range areas for
all livestock operators on a free access and free of charge basis. Unfortunately,
this policy has also included the project areas. On
December 22, 1998 some 580,000 sheep entered the Co-operative area with
the major concentration on the 8,000 ha of improved and exclosure rangeland.
More than 90% of Co-operative members took advantage of the grazing, but
also many large flock owners from up to 100 kms away trucked in sheep.
Fortunately, the incursion of the large numbers of sheep into the improved
areas took place at a time of year when plants were dormant, so that although
there was damage from the sheer numbers trampling the area, soil disturbance
by vehicles and shrub removal for fuel, it remained limited. The project
elaborated a drought management plan with Co-operative members in order
to remove sheep and households before the Spring regrowth of the range. Results Gazelle and oryx have been re-introduced and released into a fenced 1,000 ha area within the 22,000 ha Talila Reserve, which is currently managed for both camels and wildlife. The Reserve has become a focus of attention for the local population as well as providing some employment opportunities, and is also drawing considerable interest at a national level. Benefiting from two years of better than average rains, the project has been able to demonstrate excellent regrowth in exclosure areas and also excellent germination and growth of plants in improved areas. The improved areas served as demonstration plots with standing biomass of more than 400 kg/ha of dry matter from annuals alone. In December 1998 and January 1999, more than 7,000 tons of dry matter were cropped from the project area saving the Bedouins some 26 to 50 M Syrian pounds in terms of replacement feeds. The 1998/99 drought situation also illustrated some of the problems of working on rangeland improvement projects where the land is State owned and where traditional systems of range management by Bedouin herders have been largely replaced by free access, by the emergence of large commercial livestock owners and where systems of rapid trucking of sheep and supplementary feeding and watering of stock are common. But it was also a useful event to demonstrate the important role which local range management groups can play under such difficult circumstances. Lessons
learned
-
by raising population awareness of the environment,
-
through eco-tourism providing a possible alternative income source,
-
through complementary grazing habits with livestock ensuring a more balancedgrazing
of the rangelands, and
-
serving as strategic grazing reserves for livestock in drought emergency
situations;
The
project has been able to demonstrate to Government that, with the co-operation
of the local Bedouin population, rehabilitation oflarge
areas of the Al-Badia Steppe is possible, but also to illustrate the necessity
of urgently addressing the issues associated with free access of all to
all areas of land, the effects of drought and the need for preparing drought
contingency plans. Thetotal number
of sheep, overstocking and issues associated with subsidized feed are other
matters that will need to be addressed. The focus of future project activities
will be on selected rangeland site management improvement and rehabilitation,
with the selected areas managed by Bedouin organizations. As a large IFAD
funded project, which is currently being planned, will endeavour to develop
larger areas of the Al-Badia rangelands, then the lessons learned by the
present project should have direct application.
Case
Study 2 - Kazak herders, winter feed and transhumant systems in Altai Prefecture,
Xinjiang, China
The
rearing of livestock using transhumant production systems is the main land
use and livelihood in large areas of the arid and semi-arid temperate zones
of Asia. One of the major constraints to improving livestock production
and family incomes (Li-Menglin et al, 1996) is the lack of feed
during winter and early spring which reduces the number of animals that
can be carried through the winter and also means that pregnant breeding
stock may be at their most vulnerable in the period of lowest feed availability.
Attempts have been made in a number of countries to permanently settle
nomadic people often with less than desirable social consequences. This
project attempted to provide settled bases for herders where fodder for
the winter period is produced and where education and social facilities
for the herders' households are provided, but where for the major part
of the year the traditional transhumant system is followed.
The
context
AltaiPrefecture
is located in the northern part of Xinjiang Uygur Autonomous Region in
China near the border with Kazakstan and Mongolia. Bounded on the north
by high mountains and cut off from southern Xinjiang by a large expanse
of desert and semi-desert, this is an area with a markedly continental
climate, hot summers, very cold winters, snow and low rainfall. The mean
minimum temperature for January is -26 oC and the mean maximum
for July is 30 oC. Precipitation, which mainly falls as snow,
ranges fromless than 100 mm p.a.
on the plains to more than 600 mm p.a. on the high pastures, where the
problem of high winds, snow and spells of extreme cold, with temperatures
of less than -40 oC, means that many areas of high pasture are
open for less than 3 months each year.Of
the total area of 11.8 M ha, more than 9.8 M ha are pastoral and over half
of the population is engaged in livestock farming (dominated by transhumant
systems) which contributes nearly 60% of the value of agricultural production
in Altai.
The
main livestock are cattle, sheep, goats, horses and camels, with sheep
and cattle being the most important. Most Kazak herders follow a transhumant
way of life with good summer grazing for their stock on lands above 1,
300 m limited to only 2.5 to 3 months per year (late June to late September).
In spring (April to late June) and autumn (mid-September to end November),
grazing occurs on the heavily grazed transition routes and winter grazing
(December to end March) occurs on the desert plains. The transhumance route
is long, 180 to 200 km from the desert plains to the high summer pastures.
The
project
A
number of rivers and areas of relatively flat land provided the base for
an irrigation-based solution to the winter feed problem. Over
the last ten years, a development programme has been implemented to produce
and conserve fodder by cultivating over 20,000 ha of irrigated land for
hay. The production of lucerne (Medicago sativa) on the irrigated
land was assisted by WFP and UNDP/FAO.Starting
in 1988, work was begun at Burjin, Fuhai and Altai to produce "through
irrigation by gravity of 34, 425 ha of land, large quantities of hay, expected
to reach 130, 000 tonnes per year at full development, and to settle 8,
650 families through the allocation of irrigated land" (Li-Menglin et
al, 1996). By 1997, some 6, 100 Kazak households had been settled,
and 32, 000 ha have been developed, providing 20, 000 ha of alfalfa (Medicago
sativa) pasture. The average farm size is 3.7 to 4.3 ha, producing
annually about 18, 000 kg of hay from 3 ha (with the remaining land utilized
for wheat, maize, beet or sunflower) with a house for winter quarters for
the family and for those who remain on the plains for haymaking in summer
while the livestock are away on the summer pastures.
Usually a proportion of the wheat, soybean and sometimes lucerne is sold.
A number of farmers grow maize solely for making into silage. With
26,700 ha of existing alfalfa land and the newly established 20, 000 ha,
the present area in Altai Prefecture is some 46, 700 ha and there are plans
to establish another 20, 000 ha under the Ninth Five Year Plan.
Results
Visitors
to the area can quickly appreciate the degree of success of the project
in transforming former (Gobi) desert areas into productive irrigated farms
and herders into herder/farmers. The project has had a very big impact
in Altai and is accepted as a model for further Kazak herder resettlement
schemes (Anon, 1992). The findings of the 1995 evaluation mission were
that "the project has attained its ambitious targets. An area of 30,218
ha is under irrigation and settlement of 7,550 Kazak herdsmen is proceeding
on schedule. Food security for the region as well as household food security
of the target population has been dramatically increased without dismantling
the traditional socio-economic system upon which livestock transhumance
is based.The project's beneficial
impact on living conditions is evident and has resulted in a steady increase
in family incomes and access to education and health facilities. However,
the future of pastoral farming in the region is ecologically fragile because
of the constant threat of the "salting-up" phenomenon. Proper drainage
maintenance and efficient water management are crucial. Livestock pressure
on transitional pastures will also need to be monitored carefully. Therefore
sustainability is heavily dependent on a continuous and scrupulous management
of the environmentally sensitive components of the project" (Reynolds,
1998).
Lessons
learned
The
project has successfully demonstrated the complementarity of mobile pastoralism
and sedentary agro-pastoral development. Whether the benefits so far enjoyed
by the "settled" Kazak herders (who represent more than 15 percent of the
Kazaks who live in Altai Prefecture) can be enjoyed by those who still
follow the traditional transhumant way of life year round is likely to
depend on funding from the Government of China for an expansion of the
irrigated areas.
Case
Study 3 - Pastoral risk Management in Mongolia
In Mongolia, as in a number of countries in transition from a centrally planned to a market economy, there has been a marked reduction in the involvement of the state in providing services. Decollectivisation has often resulted in increased rural poverty. This project has attempted to elaborate a framework to reduce rural poverty and to prepare for disaster situations as part of the pastoral production system.
The
context
Mongolia
covers 1.5 M km2 and, with a population of 2.4 M people, is
one of the least densely populated countries in the world.The
extreme natural conditions in Mongolia, characterised by low precipitation
rates and long cold winters, have fostered a long tradition of nomadism
and extensive animal husbandry. After pure nomadism was brought to an end
through mass collectivisation and sedentarization in the early 1930s, the
pastoral production sector was dominated by specialised state farms and
central planning for more than 50 years. Decollectivisation, which started
in 1989, led to the distribution of farm assets and animals among all state
farm members (Property Privatisation Law, 1991). Since then almost every
herding family has established its own fixed winter and spring camps, with
stockyards and watering points. At the end of 1997, Mongolian rangelands
carried some 31.3 M large farm animals, the highest livestock population
since transition. In 1998, more than95
% of the animals were privately owned. Their products contributed almost
70% to the total agricultural outputs.
However,
in spite of the growth of the national herd and the private ownership of
animals and assets, pastoralists are facing severe socio-economic problems.
The shift from state to market provision of most services, the increase
in the role of markets in economic life in general and the redefinition
of the degree to which the state will, or is able, to provide a social
security safety net, have fundamentally altered herder’s living conditions,
and has led to severely reduced government services in the countryside.
Herders now carry the full burden of economic, social and environmental
risks. The incidence and negative consequences of vulnerability to risks
and poverty have increased, especially in the dry steppe areas where pastoralism
is the predominant way of life. Depending on the measure used, between
one quarter and a half of all rural households are now considered poor.
Recognising the problem, Mongolia launched a national Poverty Alleviation
Programme in 1993, which focused on urban areas initially but also started
to work in the countryside through Local Development Funds in support of
local income generation activities. Its impact on the herding economy (as
opposed to the urban poor in provincial/district centres) however, has
so far been very limited.
The
project
Within
the above context, the FAO project “Rural Development in Pastoral Areas
in Arhangay Province”, in 1996/97 participated in the drafting of a national
poverty alleviation programme for pastoral areas. In close collaboration
with IFAD, an experimental programme to analyse and fight rural poverty
was set-up, field-tested and designed for wider application and follow-up
(by IFAD). Its main interrelated components which were identified in a
participatory way together with the local herding communities were: (a)
restocking of poor herders on an in-kind credit basis through redistributing
locally available animals from wealthy to poor herding households; (b)
testing the viability and requirements of vegetable production for poor
district centre inhabitants taking into account the short growing period
of 90-100 days; (c) assessing the nature of herding risks and risk management
strategies; (d) identifying options to improve livestock productivity;
and (e) fostering economic alternatives through existing credit lines.
The project elaborated precise methods, criteria, and institutional mechanisms
to identify, in a participatory way, the local poor and needy. It supported
the establishment of institutional mechanisms to select and distribute
animals to poor herders; it distributed vegetable seeds and tools to poor
households in the district and provincial centres; and it arranged locally
available skills training and knowledge transfer. Broad participation and
the initiative of herders as well as of vegetable producers led to an encouraging
success and broad replication of the tested strategies. In the year following
the test phase the number of voluntary participants more than doubled.
The IFAD follow-up programme has now been operating successfully in Arhangay
for two years with constantly increasing numbers of participants. It is
going to expand into a second province in 1999.
Lessons
learned
Case
Study 4 - Rural Development at N’Nguigmi in Niger
Rural
development projects are complex and the adoption of a people's participatory
approach will involve different time frames and approaches to those traditionally
used. This project has already gone through several phases and has worked
largely through a number of specialised NGOs to improve existing (pastoral)
production systems and promote income-generating activities.
The
context
The
province or "arrondissement" of N’Nguigmihas
a total area of 118,000 km2, of which 84,000 km2
are desert areas. The population in 1996 was estimated to be 31,000 inhabitants
with an annual growth rate of approx. 1.0%, which means that by 2016 the
population will be over 38,000and
60% of them will be young people. Large numbers are still mobile since
in one out of every two years the forage availability for livestock is
insufficient. Only 1% of the adult population is literate. Water is the
main limiting factor. The animal population consists of 142,000 cattle,
200,000 camels, 367,000 sheep and 374,000 goats. Natural resources are
degrading very rapidly and Lake Chad is retreating.The
project selected 7 territories based on agroecological conditions and in
consultation with the population (and not with the administration or the
village chiefs) planned and started different activities according to the
specific situations. Since it started in 1984, the project has passed through
a number of phases and experiences.Of
12 wells built in 1984 only 3 are still operating due to salinization problems.
Oversized cereal granaries were built during the second phase of the project
and subsequently abandoned, and rehabilitated areas and demonstration sites
were established (with the participation of poor people) too far from villages
and therefore failed to be active demonstration sites.
The
project
From
1995, a new phase of the project started with an “approche terroir” strategy.
In the framework of decentralization and supported by mechanisms of continuous
consultation, the final objective was not the identification of specific
solutions,but to help the population
in adopting instruments for better use of their natural resources. As well
as Government and FAO involvement, the project has subcontracted the main
components of the project through specialised NGO’s.
Focus
has been on the development of pastoral (and agro-pastoral) resources,
through the improvement of existing production systems and promotion of
income generation activities. Since the elaboration and organisation of
self-determination by the communities is a slow process,“key
entrance activities” to gain the confidence of the population were necessary,
such as the construction of new wells and village shops and dune stabilization.
The development of the animal production system ("filiere elevage") was
realised through “key entrance activities”such as vaccination campaigns,
health surveillance along the border with Lake Chad, and training of technicians
in health control. Also a financial mechanism to support income diversification
activities was started.
Lesson
learned:
Overall
Conclusions
While
the some of the lessons learned were different for each case study, there
were a number of common features which emerged.
(i)
The main lessons learned were both technical and socio-economic and it
is clear thatthey must be considered
together in rangeland development programmes.
(ii)
In all areas governments must focus on the issues associated with land
tenure, grazing rights, free access of all to grazing lands, state ownership
of lands and the breakdown of traditional systems;
(iii)
To varying degrees the problem of animal numbers has to be addressed in
all areas. The provision of winter feed to enable more animals to be carried
through the winter will place greater pressure on spring, summer and autumn
pastures and the situation needs to be closely monitored. Uncontrolled
stock numbers is a key issue both for improved conservation of rangelands
and for improved incomes.
(iv)
In many countries rich businessmen are buying large numbers of livestock
as an investment and grazing the rangelands often with severe consequences.
It may be necessary to adopt a different approach for traditional herders
and new city-based pastoralists.
(v)
The population in the project areas, the herders, the pastoralists, women
etc. must have a major stake in any project. Although implementation may
be slower, and the process of dialogue with the people involved protracted,
long-term success depends on full people's participation. Many examples
can be given of apparent short-term success in terms of range improvement
etc. but longer term sustainability of the rangelands is not achieved without
taking note of the aspirations of the local population;
(vi)
Full people's participation in rangeland development will require a major
focus on training of technicians and the local people, as well as in-built
feedback mechanisms which enable adjustments to be made during project
implementation;
(vii) The importance of using "key entrance activities" to gain community confidence has been highlighted and is likely to be a feature of most rangeland development programmes where a participatory approach is adopted; (viii) To increase the chances of success in large scale development programmes there is a need to initiate small pilot projects and extrapolate from the more successful; (ix) NGOs can have an important role to play in the implementation of pastoral development projects, but the most appropriate NGO must be selected; (x) It is possible to successfully settle pastoralists, without destroying their pattern of life, as long as it is recognised that their survival depends upon maintaining their overall mobility for a portion of the year so that the flexibility remains in their system to exploit natural resources; (xi) The concept of a settled base for transhumant herders can work well by providing extra feed for feed shortage periods (from intensively managed fodder production areas) and increasing incomes, as well as providing a base for the provision of services (such as education, health etc.). The concept is particularly favourable for families, women and children. (xii) In certain situations, the creation of wildlife reserves can have very positive effects in terms of raising awareness about the environment (including rangelands), providing alternative income sources and ensuring better integration of wildlife and livestock; (xiii) In centrally planned economies, with a long tradition of nomadism and extensive animal husbandry, where decollectivisation of large state farms is underway, a new class of rural poor (unskilled herders) is being created with herd sizes below the viability threshold and with inadequate local and state organizations and support mechanisms. (xiv) The problems of rangeland use are long-term yet most development projects and programmes are far too short in duration e.g. 3 - 5 years is common. Donors, government agencies and technical agencies like FAO must begin to put the case for longer duration projects (or a series of linked projects) which stand a better chance of success. Governments must also be fully committed to providing the resources needed over the long-term and be willing to take appropriate political and economic decisions that may be required for the sustainability of rangelands and for the long-term benefit of the peoples dependent on these areas; (xv) The big challenge for FAO and other agencies is how to operate in a global environment and yet be sufficiently flexible in the face of existing diversity to implement specific solutions in given situations; (xv) Changing institutional, economic and marketing conditions - nationally, regionally and globally - will have a significant effect on rangeland use in the coming decades. With globalisation, decentralisation and liberalisation, the focus on technological development will have to be in parallel with social, environmental and ecological considerations. References Anon. (1992). Jinshan Bright Pearl. China, Xinjiang No. 2817 Project, 88p. Behnke, R. and Scoones, I. (1992) Rethinking Range Ecology: Implications for Rangeland Management in Africa. The World Bank; Environmental Working Paper No. 53. Behnke, R., Scoones, I. and Kerven, C. (eds.) (1993). Range Ecology at Disequilibrium: New Models of Natural Variability and Pastoral Adaptation in African Savannas. Overseas Development Institute, London. De Haan, C. (1995). Rangelands in the Developing World. Proc. Fifth International Rangeland Congress, 180-184. El-Shorbagy, M.A. (1998). Impact of Development Programmes on deterioration of rangeland resources in some African and Middle Eastern Countries. Chapter 5 in Drylands: Sustainable Use of Ranglands into the Twenty-First Century edit. Squires, V.R. and Sidahmed, A.E., 45-70. FAO (1995). Community Participation in Range Management for Semi-Intensive Sheep Production in the Near East: A Case Study for Maín Grazing Area in Jordan. FAORNE, 56p. Li-Menglin, Yuan Bo-Hua and J.M. Suttie (1996). Winter feed for transhumant livestock in China: the Altai experience. World Animal Review, Number 87 (1996/2), 38-44. Mirreh, M.M. (1999). GCP/SYR/003/ITA - An illustrated booklet of project activities and progress. Project GCP/SYR/003/ITA, 33p. Pratt, D.J., Le Gall, F. and De Haan, C. (1997). Investing in Pastoralism: sustainable natural resource use in arid Africa and the Middle East. Washington, D.C. World Bank, 1997. World Bank Technical Paper. ISSN0253-7494. no. 365. Reynolds, S.G. (1998). Kazak herders, winter feed and transhumant systems in Altai Prefecture, Xinjiang, China. In: Sustainable Himalayan pasture and fodder production systems; present problems and prospects. Proceedings of the third meeting of the Temperate Asia Pasture and Fodder Working Group, 9-13 March, 1998, Pokhara, Nepal, (in press). Scoones, I. (1995). Living With Uncertainty. New directions in pastoral development in Africa. Intermediate Technology Publications. London, 210 p. Sidahmed, A.E. (1993). Viewpoint: Do we need new terminologies in rangeland management? Rangelands 14(4): 201. UNSO (1994). Pastoral Development in Africa, Proceedings of the first technical consultation of donor and international development agencies, Paris, 13-14 December 1993, UNSO/UNDP. Zaroug, M.G. (1995). Rangeland. In: Sustainable Range-Dependent Small Ruminant Production Systems in the Near East Region. FAORNE, 6-51. |