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Adaptation, conflict and cooperationin pastoralist East Africa: a case studyfrom South Turkana, KenyaJeremy Lind aa Paper Prepared for CICERO (Centre for International Climate andEnvironmental Research-Oslo/Senter for klimaforskning), April 2003Published online: 03 Jun 2010.
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Conflict, Security & Development 3:3 December 2003
Analysis
Adaptation, conflict andcooperation in pastoralistEast Africa: a case study fromSouth Turkana, KenyaJeremy Lind
Paper Prepared for CICERO (Centre for InternationalClimate and Environmental Research-Oslo/Senter forklimaforskning), April 2003
The control and management of resources is the role of resources in conflict. The notion
that resource uses are socially embeddedan implicit focus of many recent studies that
and politically contingent underlines a keytrace the role of environmental factors in
argument in the paper that adaptation is athe onset and duration of conflict. Accord-
ing to the resources scarcity approach, as contentious process and is tightly linked to
resource struggles that are laden with ma-scarcities of natural resources worsen they
become unmanageable leading to violent terial and symbolic importance. It is argued
that social relations and political forcesconflict between groups competing to use the
shape different vulnerabilities, enlarging op-same resource(s). However, the resources
tions for some to adjust to environmentalscarcity perspective is misleading by de-
changes while potentially limiting optionsemphasising the socio-economic and politi-
for others. A case study of conflict andcal factors that are crucial to understanding
cooperation among interacting groups ofcontested uses and control of resources. This
paper introduces the concept of adaptation livestock herders in Turkana, Kenya lends
contextual support to these views.as an entry point into debates surrounding
Jeremy Lind is a doctoral student in the Department of Geography, King’s College London.
ISSN 1467-8802 print/ISSN 1478-1174 online/03/030315-20 2003 International Policy InstituteDOI: 10.1080/1467880032000151617
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316 Jeremy Lind
Introduction
A short tale of crisis and response introduces the theme of this paper that the resource
uses and social relations underpinning adaptation to environmental change are of
central relevance to cracking the conundrum of conflict Africa. In 1999–2000, drought
crippled Turkana District, Kenya’s northwest frontier region bordering Uganda, Sudan
and Ethiopia. It was one of many in a successive string to affect this insecure and violent
arid and semi-arid landscape inhabited predominantly by nomadic Turkana pastoralists.
By November 1999, drought and food insecurity in Turkana had captured the imagin-
ation of ‘down-country’ Kenyans, who were shocked by evocative images of suffering
aired on the Kenya Television Network (KTN).1 The chilling images of starving Turkana
were of scandalous proportions. Kenya’s leading daily paper, the Nation, soon had its
turn, infamously featuring a naked young Turkana girl with a swollen belly under a large
headline reading ‘Agony and Death’. Aro Koriang, or ‘famine girl’ as the pictured girl
became known across Kenya, was the poster-girl for the ‘Nation Turkana Famine Relief
Fund’, a private initiative co-ordinated by the Nation Media Group, owners of the
Nation. Headquartered in fashionable and modern twin office towers in downtown
Nairobi, the Nation Media Group owns newspapers in other East African countries, as
well as radio and television stations.
Kenyans, appalled and embarrassed by the level of suffering in Turkana, gave to the
Fund generously. The Nation routinely featured pictures of preparatory school children
in Nairobi standing beside bags of relief maize purchased by the Fund and bound for
Lodwar, the administrative and commercial centre of Turkana District. Meanwhile,
Aro’s progress was regularly updated in the Nation. The Nation Media Group covered
the expenditures of her rehabilitation at the exclusive Gertrude’s Garden Children’s
Hospital in the up-market Nairobi neighbourhood Muthaiga. Wilfred Kiboro, the Chief
Executive of the Nation Media Group, commented triumphantly at the time of Aro’s
release from hospital, ‘The recovery of this girl shows what we can achieve if we are
committed to alleviating poverty.’2
To its credit, the Nation’s response to the situation in Turkana in 1999–2000 was
concerted and well intentioned. In addition to co-ordinating a massive public relief
appeal, regular political cartoons and commentaries in the Nation chided the Kenya
government for not responding sooner to the Turkana crisis.3 However, the Nation in
particular and Kenya’s popular media more generally can be faulted for attributing the
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Adaptation, conflict and cooperation in pastoralist East Africa 317
Turkana famine to drought. Popular media outlets in Kenya emphasised that the
Turkana environment was inhospitable and suffered chronic stress, a modern-day ‘land
of the living dead’.4 Invariably, these perceptions helped to shape a public discourse in
Kenya that the famine was understandable to a degree, a consequence of Turkana’s
uncommonly bleak and unforgiving environment. Alternatively, little effort was made to
excavate and explain the far more complex social and political-economic realities in
Turkana that contribute to food insecurity and conflict. Conflict in Turkana is ‘low-
intensity’, characterised by localised competitions, violent livestock theft (‘raids’), ban-
ditry and seemingly random violence. However, buried beneath the images of human
suffering and environmental ‘collapse’ rests a spider-web of social relationships and
resource uses that is the groundwork for adaptation.
Sensitive to the political and economic differentials that weigh heavily on capacities to
adapt, this paper aims to inflect conflict into analysis of adaptation to environmental
change. Building on anthropological work on Turkana herders, my interest in adaptation
is to understand ‘mechanisms of adjustment or patterns of variation, including processes
that contribute to or limit variation’ (Little et al., 1999, p. 7). Beyond identifying and
cataloguing a range of pastoralist adaptative techniques there is growing scholarly
attention to the socio-economic and political context in which adaptive responses and
the vulnerability of differently positioned actors are determined (Little et al., 1999, p. 7).
At the outset, it is appreciated that conflict increases the susceptibility of different actors
and groups to environmental change (while at the same time improving the prospects
of others). Conflict can upset the delicate resource uses and societal relations that
underline adaptation. The threat of conflict and violence can make movement between
key resource areas untenable and the areas themselves inaccessible. By restricting
mobility and access to important key resources, therefore, conflict and violence can
worsen vulnerability to uncertain changes in the environment. It is also recognised that
arrangements to share control and use of resources in some contexts can serve as the
foundation for a broader peace between competing groups. However, it is instructive to
extend arguments beyond consideration of the impact of conflict on vulnerability to
environmental change to consider the role of adaptation in conflict itself. The notion
that resource uses are socially embedded and politically contingent underlines a key
argument in the paper that adaptation is a contentious process and is tightly linked to
resource struggles laden with material and symbolic importance.
In the following section I suggest the importance of different perceptions of landscape
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318 Jeremy Lind
and environmental change to explain conflict and vulnerability. This section includes a
very brief introduction to the ‘resources scarcity’ approach. Section three is an overview
of pastoralist resource use systems and societal relations. In this section I attempt to
show that loose references to a scarcity of resources is inadequate to identify and
understand the sources of conflict between pastoralist groups in East Africa. This
proposition is taken up in section four, a case study on conflict and cooperation between
herders in south Turkana. The concluding discussion consists of a summary of main
points emerging from the paper.
Perceptions of range-landscapesAn impression that African rangelands are desolate, damned and degraded is proverbial.
Turkana has long been construed as a remote and difficult place. European explorers
first navigated the Turkana rangelands near the turn of the twentieth century. Ludwig
Ritter von Hohnel, a Naval Lieutenant who accompanied the Austrian Count Samuel
Teleki on an expedition into the far reaches of northern Kenya in the late 1800s, noted
on their approach to Turkana, ‘The scenery became more and more dreary as we
advanced. The barren ground was strewn with gleaming, chiefly red and green volcanic
debris, pumice stone, huge blocks of blistered lava and here and there pieces of wood’
(Graham and Beard, 1973, p. 38). Like von Hohnel, other explorers described a barren,
drought stricken, largely uninhabited and foreboding environment. One traveller went
six days across waterless rangelands in central Turkana without coming across suitable
pastures.5 A former Turkana District Commissioner recounted a similar description. The
general appearance of the land, he wrote, was an arid plain broken by abruptly rising
rocky hills, the colour of the land being ‘that of the bare ground showing through the
cover of plants.’6 Importantly, he emphasised that the area had an unusually inhospitable
climate that he observed was largely responsible for the scarcity of range resources in
Turkana. A social scientist researching in Turkana in the 1950s described the typical state
of the Turkana plains as ‘one of bare sandy or rocky soil with a sparse intermittent cover
of low bushes, shrubs, and scattered small trees’ (Gulliver, 1955, p. 23). He observed that
the watercourses supported larger trees, but that otherwise there was a virtual absence
of permanent forage outside of mountainous areas.
The importance of early assessments of the Turkana environment can not be
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Adaptation, conflict and cooperation in pastoralist East Africa 319
underestimated. They contributed to the formation of perceptions of the Turkana
environment as harsh, bleak, degraded and threatened and that persist to the current
day. Just compare earlier assessments of the condition of the Turkana environment with
the Nation coverage of the famine in Turkana in 1999. Indeed, generations after
European explorers first visited the rangelands of East Africa, a dark perception of
Africa’s rangelands is enshrined in the discourse of numerous academic disciplines,
government policies and projects, international humanitarian efforts, popular media and
in the minds of an African and Western general public. It is informative here to consider
Said’s work on orientalism or the cultural domination of the west over the orient. He
(Said, 1979, p. 36) reasons, ‘Knowledge gives power, more power requires more
knowledge, and so on in an increasingly profitable dialectic of information and control.’
He shows how orientalism works as a hegemonic discourse, or a way of ‘dominating,
restructuring and having authority over the Orient’ (Said, 1979, p. 3). The orientalist
discourse, he argues, represents orientalism but not the Orient. In a similar way, an
overriding perception of Turkana as bleak and harsh is one way of representing Turkana
as an orientalist landscape infused with mystery, extremity and hardship.
Perceptions do more than just describe. They condition those who are unfamiliar with
the Turkana environment to accept that it is problematic and requires adjustment, and
subsequently give rise to explanations that inform the formulation of inappropriate
policies. However, it needs to be determined whose interests are served by orientalist
ideas of the Turkana landscape, and by association the Turkana people. At least the
Turkana themselves perceive their environment differently from orientalist representa-
tions that feature in the Kenya media. The Turkana landscape articulated by local
pastoralists is variable and changing, cut by numerous small streams and seasonal rivers,
and framed by mountains all supporting substantial resources for grazing livestock
(Lind, 1999). Turkana pastoralists perceive the landscape as challenging but negotiable,
a patchwork of risks and opportunities.
Preoccupation with the landscape leads to a wider discourse on the environment
determining factors of Turkana livelihoods and conflict, which in turn tie into a body
of opinion on resource scarcities. The belief that a scarcity of resources is the source of
conflict, what I refer to here as the ‘resources scarcity’ approach, has gained prominence
in conflict policy debates in recent years.7 My concern is to question the explanatory
power of the resources scarcity approach to understand conflict, and more generally to
challenge resource determinism in approaching Turkana livelihoods. I suggest that the
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320 Jeremy Lind
resources scarcity approach does not address the complexities, inconsistencies and
anomalies that colour resource struggles and that must surely nuance any abstract
conceptualisation. Rather, as Fairhead (2000) points out, conflicts that have their roots
in resource scarcities need not have anything to do with the environment. In other
words, he cautions against the causal ascription of conflict to environmental factors. In
a similar way, I suggest that the resources scarcity approach is misleading
by de-emphasising the socio-economic and political dimensions of the use and control
of resources.
‘No blood for pasture’: pastoralist resource usesand societal relationsA substantial body of research examines the condition and nature of conflict in
pastoralist areas. The control and management of resources is an implicit focus of many
of these studies, which trace the role of environmental factors in the onset and duration
of conflict.8 Variations of the resources scarcity approach are apparent in many studies
of conflict in pastoralist-inhabited areas of East Africa, according to which a combi-
nation of conjectural (ecological) and structural (political-economic) pressures leads to
violent conflict. This section critically questions if the resources scarcity approach helps
us to understand conflict and cooperation between pastoralists.
Resource uses in unpredictable rangelands
A constellation of pastoralist groups inhabit large swaths of the Great Rift Valley, a vast
area of East Africa extending southwards from Ethiopia through Kenya and into
Tanzania. Although the Valley exhibits profound ecological and ethnic diversity, its
landscapes are dominated by expansive, unpredictable arid and semi-arid rangelands.
These are inhabited largely by interacting groups of livestock herders. The viability of
pastoralist systems in these rangelands rests on the flexibility of herding units to tailor
individual responses to the social and ecological contingencies impinging on manage-
ment of herds. Given that uncertainty in East Africa’s rangelands is ubiquitous, and it
is essential to draw together an array of patchy key resources to sustain herds as the
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Adaptation, conflict and cooperation in pastoralist East Africa 321
centre of pastoralist production strategies, it is perhaps little surprising that competition
and conflict occur. The resources scarcity approach implies that as scarcities of natural
resources worsen they become unmanageable leading to violent conflict between groups
competing to use the same resource(s). However, in contrast to this reasoning,
pastoralists are demonstrably capable of peacefully managing persistent ecological stress
and recurring resource limitations.
Mobility is the essence of customary livestock grazing strategies for overcoming the
spatial and temporal variability of resources in non-equilibrium rangelands. As McCabe
et al., (1999, p. 121) contend, ‘the causes and consequences of nomadic movement lie
at the heart of the adaptive process for the Turkana.’ The flexibility of individual herding
units to reach decisions independently enables herders to carefully consider the move-
ment of livestock and labour to care for livestock in relation to fluctuating social factors
and physical changes in the environment. In particular, patches of key resources nested
within the overall environment are crucial to sustain livestock herds in dry rangelands.
Putnam (1986, quoted in Scoones, 1990) notes that, ‘grazing animals do not use all
habitats equally and … some sustain much higher impact than others. Further, different
patches of the same community type suffer different grazing pressures dependent on
their juxtaposition with other communities or geographic position.’ The importance of
patches to opportunistic livestock grazing strategies as Scoones and Cousins (1991) show
is to stabilise production seasonally and interannually.
Mobility is the means to incorporate disparate but highly productive resource patches
into an overall efficient resource use system to sustain livestock herds. Mobility draws
scattered key resource patches together into a delicate but productive resource base upon
which livestock herds can persist and grow. Western and Finch (1986, p. 87) emphasise
that ‘risks can be minimized and production maximized on heterogeneous pastures by
optimising migratory pathways between quality patches.’ Movements between different
patches require that herders be prescient and cautious in making their calculations. A
miscalculation can be ruinous in a context in which a high degree of risk permeates all
dimensions of the resource base. In physically variable non-equilibrium rangelands the
margin between profit and loss is slim.
Besides movement between key resource areas, pastoralists draw on other techniques
to seize opportunities and minimise risks related to the physical variability of resources.
One technique is to keep large herds as a reserve against environmental uncertainties,
such as fluctuations in rainfall and temperature or the threat of disease. Higher stocking
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322 Jeremy Lind
rates enable pastoralists to survive through periods when the availability of resources
ebbs and hunger is a real threat. Another technique is to maintain herds composed of
many species of livestock. Little et al., (1999) outline the advantages of the diverse herds
managed by the Turkana, which include combinations of goats, sheep, donkeys, cattle
and camels that vary with individual herding families. Species-diverse herds, they
maintain, enable herders ‘to take advantage of both high biomass productivity of small
stock and cattle, and high survival and milk yields of camels, as well as allowing them
to exploit the many layers of the complex vegetative communities of South Turkana’
(Little et al., 1999, p. 56).
The varying feeding and watering requirements of different livestock species means
that livestock managers frequently split herds into smaller units to take advantage of
specialised ecological niches that cater to the specialised needs of different livestock. In
their assessment of livestock feeding ecology in South Turkana, Coppock et al., (1986,
p. 580) found that ‘divergent patterns of habitat use were important in the spatial
segregation of stock during periods of resource limitation.’ Herd splitting itself is
another adaptive technique to physical, as well as biological variation in the environ-
ment. By splitting herds into smaller units that are scattered over a larger area of the
environment, it is easier to locate adequate resources to sustain livestock in periods when
range resources are scarce and ecological stress is high. Ellis and Swift (1988, p. 457) note
that in South Turkana, ‘as environmental stress increases, pastoralists divide their
livestock herds and accompanying human groups into smaller and smaller units. These
units move more frequently as well.’ In the same way, it is also less likely that an entire
herd will be eliminated when there is an outbreak of disease if animals are divided into
smaller units and are grazed in separate locations.
These adaptations point to the range of techniques evolved by pastoralists to temper
risks to natural calamities and to exploit patchy key resources to sustain and enlarge
livestock herds. As Cossins (1986) argues, the challenge in managing non-equilibrium
dry rangelands is not to conserve resources, but to develop resources more fully and
equally. Indeed, and casting further doubt over the suitability of the resources scarcity
approach to explain conflict, Little et al., (1999, p. 58) find that only a fraction of overall
vegetative productivity is currently being utilised by livestock herds in south Turkana.
They estimate that only 10% of the total above ground net primary productivity
(AGNPP) is utilised by livestock animals (emphasis added). Their estimation confirms
earlier appraisals of the Turkana rangelands that found degradation was not a serious
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Adaptation, conflict and cooperation in pastoralist East Africa 323
problem (see Ellis and Swift, 1988). Bollig (2000, p. 361) notes that the Baringo
rangelands inhabited by Pokot pastoralists to the south and east of Turkana carry only
50% of the livestock population compared to earlier in the twentieth century. It is
important to recognise that under-utilisation of key grazing areas can be deeply
problematic for pastoralists as unpalatable bush growth spreads into rangeland areas that
are rarely used (Hjort, 1982).
Pastoralist societal relations in the past and present
Although control over scarce resources remains perennially important in pastoralist
areas, Waller explains that a regional system of inter-locking pastoralist groups ‘creates
and preserves ecological and social niches in which communities and ethnicities may
take root’ (Waller, 1993, p. 294). A network of cross-sectional and cross-ethnic bond-
friendships is the basis of pastoralist regional systems in East Africa. Historically,
integrative contacts through bond-friendships between pastoralists belonging to different
groups acted to temper conflict (Sobania, 1990). Sobania explains that the structure of
pastoralist societies was loose, with different groups adapting to particular ecological
niches. He shows that the adaptations of neighbouring groups to the peculiarities of
separate but complementary ecological niches enabled the establishment of bond-friend-
ships across societal boundaries. Bond-friendships, in turn, were the substance binding
together the wider regional ‘resource system’ that Waller describes.
Customarily, pastoralist subsistence was founded or at least deeply dependent on the
friendships of exchange and reciprocity that underline the regional system. The network
of bond-friendships formed by pastoralists was essential to sustain herds (the basis of
pastoralist production and livelihoods) through episodic and unpredictable resource
shortages. Although the ‘sawtooth’ pattern of herd growth ‘in which the slow accumu-
lation during periods of relative calm was offset by the sharp reversals at critical times’
was inescapable for most pastoralists, integrative contacts could have a mitigating effect
on herd losses by supporting recovery (Spencer, 1974, p. 419). Conflict and competition
were indisputably an important part of the balance of power and the control of
resources by different pastoralist groupings. However, cooperation and reciprocity were
also important to pastoralist strategies for negotiating the patchy availability of key
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324 Jeremy Lind
resources. In the past, as Galaty (1993, p. 78) shows, herders belonging to different
Maasai sections came together peacefully to share resources, ‘sectional alliances allowed
for shared access to pasture outside the “home” section’. However, he also explains that
periods of relative peace between different Maasai sections historically can be seen as
precursors to ‘conflict and preparatory expansion’.
Spear (1993) contends that ethnic ideologies in East Africa were closely related to the
environment, serving to control access to resources. If so, it is instructive to understand
not only the symbolic importance of ethnic identity and ideology in the context of
resource struggles and cooperation, but their instrumental value as well. Waller suggests,
‘Rather than assume the continuity of social groups through time it may be more helpful
to establish the continuity of certain kinds of identity through which different groups
may “pass” and to examine the factors which make this possible’ (Waller, 1985, p. 349).
For at least some groups, a malleable ethnic identity enables them to make opportunity
of flux in social relations to enlarge access to resources.
Sobania’s claim (1990, p. 2) that ‘mosaics of once separate groups came together to
exploit a particular ecological zone’ can be considered in light of Waller’s argument that
the ‘ambiguity of identity aids creation of new social formations’ (Waller, 1985, p. 350).
For example, Lamphear (1992) explains that a loose corporate identity enabled the
Turkana to assimilate neighbouring groups as they expanded south and east of their
cradle-land near the border of Uganda to occupy a more expansive territory inhabited
by pastoralists, agriculturists, fishers and gatherers. Accommodation was equally import-
ant to force, for pastoralists to make opportunistic use of variable key resources.
Lamphear shows that many groups in the path of Turkana advances subsequently
‘became’ Turkana as ‘being’ Turkana was expedient to gain access to resources. This
gives credence to his contention that the proximate causes of pastoralist wars in the past
had less to do with resource scarcities than they did with differences over power
relations. Pastoralists by and large were (and still remain) effective in managing resource
scarcities, as it was noted earlier. Rather, conflict pivoted on power imbalances as
neighbouring groups came into contact and negotiated differences over ideology and
identity.
Sobania (1990, p. 9) explains that large livestock holdings provided a margin of
security against drought for livestock herders in northern Kenya historically. However,
‘disaster pushed the weakest beyond the threshold of self-sufficiency and forced them
into alternative economic strategies’. In this case, socio-economic and political factors
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Adaptation, conflict and cooperation in pastoralist East Africa 325
weakened the adaptive capacities of some herders, who were susceptible to environmen-
tal change. In the present day, research findings from East Africa show that the gap is
expanding between the capacities of wealthier and less privileged pastoralists to adapt to
environmental change, with significant knock-on effects on social relations between
herders. A closely related research finding is that the capacities of vulnerable groups to
adapt to environmental changes decline with each subsequent catastrophe. In East
Africa, as Waller (1999, p. 27) succinctly states, ‘some [pastoralists] may recover and
prosper… but others will remain impoverished, always intensely vulnerable to further
misfortune.’ In their study of the experience of drought by Ariaal pastoralists in
northern Kenya, Fratkin and Roth (1990) find that although the wealthy lost more
animals than the poor, the size of their herds was larger to begin with, meaning they
were buffered against the most serious consequences of drought. Further, they show that
drought actually increased disparities between wealthy and poor households. Possessing
larger herds and labour to care for livestock, wealthier herders were in a stronger
position to recover from drought than poorer herding units who had considerably fewer
livestock and fewer members to make effective use of the patchy distribution of
resources.
Lacking livestock is the signature of poorer pastoralists who, by their very poverty, are
excluded from social networks that operate through the reciprocal exchange of animals.
Waller (1999, p. 28) characterises the pastoralist poor as, ‘those [who] … will have either
less access or fewer resources.’ In the case of Turkana pastoralists, Broch-Due (1999)
demonstrates the all-importance of stock, which she explains are the only medium to
register and establish social relations. If being poor means lacking access to resources,
the implication is that the poor lack the capacities to adapt to environmental change, as
well. From this, it should not be construed that struggles for scarce resources are
‘normal’ or that resource scarcities are sources of conflict between pastoralists. In
contrast, the capacities of underprivileged pastoralists to contest access to and control of
resources are easy to overestimate. Instead, I propose that through a Geertzian ‘thick
description’ of the symbolic importance of resources for differently positioned actors,
combined with an overriding attention to the social-economic and political aspects of
adaptation, the roots of competition and differentiation within pastoralist groups can be
more accurately identified and understood. The following case study from South
Turkana develops these propositions further.
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326 Jeremy Lind
Conflict and cooperation in south Turkana,Kenya
Dispute has long been associated with the use of natural resources in south Turkana. Its
rangelands have a highly variable and unpredictable climate. Ellis and Swift (1988)
report frequent droughts in the South Turkana region, at least four of which were
multi-year droughts in a 50-year period beginning in 1937. The distribution of resources
is also spatially variable. As it was observed in the preceding section, grazing resources
are not spread evenly over arid rangelands, but are instead concentrated in patches along
rivers or in mountains. Elsewhere, it is noted that environmental variability results in a
high degree of political competition, ameliorated by periods when competitors relate to
one another as allies, neighbours or kin (Behnke, 1994). Similarly, relations between the
Turkana and neighbouring Pokot pastoralists have alternated between peace and open
warfare over the last century. This section considers the suitability of the resources
scarcity approach to explain conflict and cooperation between herders in south Turkana.
Traditionally, Turkana pastoralists formed reciprocal resource use agreements with
the Pokot as one technique to manage risk in resource uncertainty. In exchange for
concessions to graze animals on Pokot pastures during the dry season, the Turkana
granted Pokot pastoralists the right to take livestock to salt licks lying in Turkana areas.
These agreements were flexible and were subject to constant re-negotiation as the
condition of the environment fluctuated. The imposition of British colonial rule in
northern Kenya and the involvement of colonial administrators in inter-tribal affairs,
however, resulted in the escalation of political tensions between Pokot and Turkana
herders surrounding the use of resources. Colonial policy called for the separation of
different ethnic groups and limited their movement to areas in which they ‘belonged’
(Sobania, 1991). The separation of different ethnic groups into demarcated tribal
territories served many purposes, among them the need to exercise power and authority
over native populations, as well as to survey and control resource uses. A boundary
demarcated by the colonial government between ‘Turkana’ areas and ‘Pokot’ areas
encapsulated the policy of divide and rule that is the legacy of British dominion in
Kenya. South Turkana and West Pokot Districts belonged to different administrative
areas. Up to 1926, South Turkana was ruled as part of the Turkana Military District and
was cut off from the rest of the colony as the King’s African Rifles fought a ‘total war’
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Adaptation, conflict and cooperation in pastoralist East Africa 327
against the Turkana.9 West Pokot was part of the Rift Valley Province, and was more
integrated into the life and economy of the Kenya colony.
Boundaries were an integral part of attempts by the colonial administration to
regulate rangeland uses. Colonial authorities presupposed that pastoralists were causing
environmental degradation by overstocking the range. The destocking policy pursued by
the colonial government aimed to reduce herds to a calculated carrying capacity for a
defined area and to delineate dry and wet season grazing reserves for the use of African
herds on a rotational basis. Customary arrangements between pastoralist groups to share
resources were mostly prohibited. In a 1950 district report, the District Commissioner
for Turkana reasoned that a closed boundary was necessary for grazing control,
The determination to contain Turkana stock within the present limits of the
district and to restrict all demands for grazing concessions outside except when
conditions are really desperate, makes it necessary to deny Turkana grazing to
other tribes and to require immediate action when trespass into Turkana
occurs. The strict enforcement of this policy is also an essential part of grazing
control. The tribes most affected by the closer control now enforced are mainly
the Suk [Pokot] of West Suk and Baringo Districts who were used to
obtaining grazing and watering concessions in Turkana on demand for many
years.10
However, boundaries and the rights of herders on different sides of the border to
enter into reciprocal grazing arrangements were hotly contested between colonial officers
themselves. Officials in West Pokot preferred non-intervention, leaving issues of the
boundary to customary authorities. An ‘elastic’ boundary open to annual grazing
agreements administered by a small tribunal composed of local elders was called for.11
Turkana District officials, however, favoured a ‘hard and fast’ boundary. They wanted
to end reciprocal arrangements whereby resources were shared in the interest of strictly
regulating the use of grazing reserves in Turkana for use by Turkana herders in the dry
season. Tensions flared in the 1950s, when officials in the two districts disagreed over
whether Pokot herders could take their animals to the Kula salt lick, which lay just inside
the Turkana side of the border demarcated by the colonial government. In a letter in
July 1952 to the Rift Valley Provincial Commissioner, the Provincial Commissioner for
the Northern Frontier District (which included Turkana District) wrote,
It seems to me that what the Masol Suk [Pokot] are asking for is not a
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328 Jeremy Lind
temporary, emergency concession, such as is commonly granted in drought
years for the purpose of alleviating abnormal hardship, but authority to
extend their wet weather grazing ranges into Turkana … The country coveted
by the Suk for wet weather grazing is urgently needed by the Turkana for their
dry weather reserve, and it is therefore vital to them that, during and
immediately after the rains, it should be kept closed to stock.12
In his reply, the Rift Valley Provincial Commissioner curtly responded,
Many thanks for your letter … I am hoping to get hold of suitable ammu-
nition to reply to your letter in due course, it will be a pleasure to have an
amicable battle with you once more.13
However, the West Pokot District Commissioner reluctantly conceded to the position
of the Turkana officials, although he remained adamant that the best solution was to
allow Turkana and Pokot elders to reach an agreement on their own. Throughout this
period, conflicting messages were communicated to different herders as to their rights
to use resources in and near to the common boundary.
By carving out more distinct identities for different herding groups and associating
these with clearly defined territories, the impact of British intervention in pastoralist
societal relations in south Turkana was to limit contact between Turkana and Pokot
herders. Prior to the imposition of colonial rule, relations between the Turkana and their
neighbours were characterised by ‘reciprocal raiding’, which arguably worked against the
escalation of hostilities into wider conflict (Lamphear, 1994). Raids served to rebuild
herds following droughts and in this way to redistribute livestock to herders and herding
units in need. Lamphear (1993, p. 95) notes that occupation of new territory was a
secondary or unintended consequence of past Turkana expansions, which had more to
do with ‘impoverished individuals anxious to build up herds.’ At first glance, raiding
makes sense from the perspective of adaptation because herders can acquire animals to
participate in the bond friendships and kin networks that are so crucial to living with
resource uncertainties. Like Lamphear shows for the past, Bollig (1990) contends that
conflict between Pokot and Turkana pastoralists in the current day is not aimed at
increasing territory (and thereby access to resources) as it actually exacerbates resource
scarcities. Instead raiding is used by younger Pokot age-sets to increase their holdings of
livestock. Livestock, he explains, are scarce only in relation to the high consumption of
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Adaptation, conflict and cooperation in pastoralist East Africa 329
livestock by younger men to pay as ‘brideprice’, or in initiation and promotion
ceremonies.
Thus, the suggestion that conflict between Turkana and Pokot pastoralists is a
competition for scarce grazing resources is problematic. Resource scarcities are worsened
because of conflict; insecure areas are avoided and more secure pastures are badly
overgrazed in some situations. Turton (1991) notes that the techniques adopted by the
Mursi agropastoralists in south-western Ethiopia to increase their physical security and
to protect their animals from violent theft have reduced the effectiveness of their
agro-pastoralist system, as well as increased their long-term vulnerability to environmen-
tal change. This is the paradox of conflict, in pastoralist areas as well as elsewhere.
Whereas raiding (at least traditionally) enables some herders to acquire animals, it also
contributes to a sense of insecurity that makes it difficult for other herders to make full
use of the resources they depend on to live with resource uncertainties. There are
winners and losers of conflict, cautioning against any generalisation of the costs and
benefits of conflict in terms of capacities to live with and adapt to environmental change.
There is growing interest in understanding how conflict makes sense to differently
positioned social actors, rather than seeing conflict as the dissipation of otherwise
peaceful societal relations. Keen (n.d., p. 1) explains that one of the limitations of past
approaches to conflict and violence is that they have ‘tended to regard conflict as,
simply, a breakdown in a particular system, rather than as the emergence of another,
alternative system of profit and power.’ Turton (1992) explains that warfare is ‘a means
by which the very idea of [an ethnic group] as an independent political unit … is created
and kept alive’ (Turton, 1992, p. 32). He contends that warfare is a form of ‘ritual’
resolution of disputes between the Mursi and their neighbours, ‘Warfare is a reciprocal
activity by means of which groups assert their independence of each other and enter into
orderly (rule governed) relations. Viewed in this way, then, warfare is not a breakdown
in “normal” political relationships, but instead is the very underpinning.’ As he suggests,
conflict is not illogical or an aberration from otherwise peaceful relations but sustains
the Mursi as a political unit.
In East Africa, many have observed a new dynamic underpinning raiding in pastoralist
areas. For example, the Nation reported in July 1999 that a criminal cartel including
well-connected traders, politicians and officials from the provincial administration was
co-ordinating raids in Turkana and surrounding districts ostensibly to obtain livestock
to sell to abattoirs in Nairobi and other urban centres.14 Hendrickson et al., (1998, p. 9)
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330 Jeremy Lind
also detail the emergence of ‘predatory raiding’ in Turkana, which they claim is
motivated by powerful actors outside Turkana whose intention is ‘to procure cattle in
vast quantities either to feed warring armies or to sell on the market for profit.’
Therefore, for some conflict makes sense. Some suggest that conflict be explicitly
addressed and accepted as inevitable rather than ignored or be viewed as abnormal
(Scoones, 1994). To this it can be added that conflict should not be seen as the desperate
action of impoverished herders who attempt violently to claim scarce resources in an
increasingly degraded environment. Instead, conflict needs to be situated in the dynamic
social, economic, ecological and cultural fields from which it arises.
ConclusionThis returns us to the vignette of the Turkana famine that opened this paper. Kenya’s
popular media for all its well-intentioned coverage of the situation in Turkana (and
while acknowledging the secondary role of government incompetence for failing to
address the crisis) incorrectly portrayed all Turkana as helpless victims of an unforgiving
natural calamity, but they are not. Although drought is indisputably an important factor,
the tragedy that befell Turkana in 1999, and that threatens again in 2003, is traceable to
the socio-economic and political realities in Turkana that foretell greater fortune for
some, therefore greater capacity to respond to and adapt to environmental changes, and
greater loss for others, for the poorest who are vulnerable and ultimately left beyond the
pastoralist fold. By casting the Turkana landscape as inhospitable and bleak, the political
aspects that are so important to understanding how distinct and different vulnerabilities
arise, as well as why capacities to adapt are variable, are glossed over. ‘Why are some
pastoralists able to adapt and prosper at the same time that other pastoralists—possibly
from the same family or group—are unable to cope and become destitute?’ is a guiding
question that should inform any attempt to respond to situations like the one in
Turkana.
While the observation is not new that adaptation to environmental change is socially
mediated and politically contingent, this paper has sought to relate the social and
economic exigencies of adaptation to a broader debate on the role of resources in
conflict. In doing so, I suggest that a livelihoods approach that accounts for adaptation
offers guidance to understanding resource struggles and is a helpful alternative to the
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Adaptation, conflict and cooperation in pastoralist East Africa 331
resources scarcity perspective to explain the origins and nature of conflict and co-
operation between pastoralists in East Africa. The resources scarcity perspective is
misleading by de-emphasising the socio-economic and political factors that are crucial
to understanding the use and control of resources. Rather, studies of vulnerability and
adaptation in the context of environmental change and appreciative of politics proffer
many explanatory insights to enrich and inform the burgeoning interest in the resource
origins of pastoralist conflicts. Competition is ingrained in adaptation. As it is seen, social
relations and political forces shape different vulnerabilities, enlarging options to adapt for
some while potentially limiting options for others.15 It is informative to view adaptation
as a process, one that is dynamic and significant both materially and symbolically and
that results in different vulnerabilities between and within herding units.
The logical beginning of any analysis of competition involving pastoralists is to
recognise that there is a compendium of variables (not only resource based) nested
within specific geographical, social and historical contexts and that are converging at
different points in time leading either toward cooperation or conflict. The more
important ones examined in this paper include the size of herds, as well as effective
command of labour to care for livestock, both of which are integral to pastoralist
adaptive capacities. Following from this, it is worth noting that the groundswell of
interest in the role of resources in pastoralist conflicts conceals the spectrum of other
sources of conflict—social, political, economic, legal, historical and symbolic. It also
distracts attention from non-violent and peaceful arrangements between pastoralists to
share control and use of key resources, as well as livestock and labour with bond-friends
and kin.
However, it is worthwhile, as well, to appreciate that resources play a decisive role in
the onset and trajectory of many conflicts. Politically saturated competitions to gain
access or ownership of resources either directly (i.e. livestock theft) or by assembling
extensive social networks are common for pastoralists. Social networks in the form of
extensive bond-friendships and linkages with kin are vital to maintain or claim rights to
access, use or own resources that underpin production strategies to enlarge wealth and
prolong subsistence. At the same time, resources are vital to inscribe and establish
bond-friendships and relations with kin. Access and ownership of resources in pastoralist
contexts is essential to preserve social bonds that bridge different vulnerabilities and can
decide the fate of individual herders.
The politics surrounding adaptation can result in greater overall vulnerabilities to
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332 Jeremy Lind
environmental change and accelerate the processes leading to vulnerability and loss,
increasing the attrition of the poorest pastoralists. The growing disparity between
wealthier and poorer pastoralists can complicate efforts to bridge vulnerabilities and link
different individuals and groups into a responsive social network. As the poor lose their
entitlements to access, use or own resources, they are excluded from the reciprocal
exchanges that link the wealthy and the underprivileged and that are pivotal to recover
from loss, as it was seen. It is vital to account for the range of formal and informal
institutions and policies that govern societal relationships and that configure the options
available to different individuals and groups to adapt. Finally, assessment of the
processes leading to the concentration of the assets, resources and rights that enable
effective adaptation is indispensable to any explanation of conflict and cooperation
among pastoralists. These must further consider how the resource uses that underpin
adaptation are continuously, incrementally or suddenly changed in response to shifts in
societal relations and political and economic forces.
Endnotes1. KTN is an independent station that is broadcast in
Kenya’s main urban centres, Nairobi, Mombasa,
Kisumu, Nakuru, and Naivasha.
2. Nation. 13 June 2000. Nairobi.
3. See the Nation. 28 November 1999. Nairobi.
4. Nation. 22 November 1999. Nairobi.
5. Ref. PC/NFD1/8/1. Nairobi: Kenya National Archives.
p. 15.
6. Ibid. pp. 3, 5.
7. Homer-Dixon has developed models to demonstrate
the linkages between conflict and scarcity of renewable
resources. A haunting view of environmental decline
leading to conflict underlies his models, which centre
on the interaction of three sources of renewable re-
source scarcity, including environmental degradation,
population growth, and the unequal distribution of
resources (Homer-Dixon, 1999). In one interaction,
‘resource capture’, environmental degradation and
population growth encourage powerful groups within
society, who anticipate worsening environmental
scarcities, to ‘capture’ resources for their benefit. In a
second interaction, ‘ecological marginalisation’, popu-
lation growth and unequal resource access interact,
leading to environmental degradation and to increased
environmental scarcity (Homer-Dixon and Blitt, 1998,
p. 6). They explain that resource scarcities give rise to
a number of intermediate social, political and econ-
omic disruptions, including constrained agricultural
productivity, constrained economic productivity, mi-
gration and displacement, social segmentation, and the
collapse of legitimate institutions. These disruptions,
they explain, lead to conflict.
8. In particular, see Bollig, 1990; Markakis, 1993; Fukui
and Markakis, 1994; Hendrickson et al., 1998; and Lind
and Sturman, 2002.
9. See Lamphear, 1992.
10. Turkana District Annual Reports. 1950. Nairobi: Kenya
National Archives.
11. Ref. LND. 16/1/2.II/263. Nairobi: Kenya National
Archives.
12. Ref. LND. 16/5/N.18. Nairobi: Kenya National
Archives.
13. Ref. LND. 16/1/2/59. Nairobi: Kenya National Archives.
14. Nation. 20 July 1999. Nairobi.
15. See the literature on the political economy of resource
access and use. For examples, see Blaikie, 1985; and
Bryant, 1991.
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