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A major question that has emerged from the research and discourse on
community-based natural resource management in southern Africa is whether
traditional rules comply with generally accepted principles of common
property management. In other words: do traditional institutions offer
a solution for the sustainable management of natural resources held
in common? This paper traces the emergence of traditional institutions
from the pre-colonial times to the present, and draws a comparison with
one fundamental principle of common property management: exclusivity
of resource use. Evidence from Zimbabwe shows that traditional rules
governing natural resources contradict this principle. The study suggests
that the gap between traditional institutions and design principles
for sustainable common property resource management can be bridged by
making small continuous institutional changes over an extended period
of time. It also recommends that longitudinal studies based on
historical precedent rather than contemporary narratives and
cross-sectional studies are required for informed policy decision-making
in order to transform traditional institutions. INTRODUCTION Bromley (1991) has argued that, with the advent of colonialism and
markets, the spread of private landand the attendant individualisation
of village lifehas undermined traditional collective management
regimes over natural resources.[1] In this
interpretation of history, the individualization of property led to
the breakdown of traditional authority and community regulation over
common resources. As a result, common property resource regimes degenerated
into open access. Some scholars therefore believe that a return to the
pre-colonial situation, when traditional institutions once prevailed,
will empower communities to manage their resources more sustainably.
The implicit assumption being that traditional systems of land tenure
were characterized by collective action and common property management
regimes.[2] The first difficulty with this view is that it differs materially
from the literature on the reinvention of tradition.[3]
Ranger (1983), for example, maintains that: "The most far-reaching inventions of tradition in colonial Africa
took place when the Europeans believed themselves to be respecting age-old
African custom. What were called customary law, customary land-rights,
customary political structure and so on, were in fact all invented by
colonial codification."[4] Ranger does not imply that pre-colonial African societies did not
have valued customs, identity and continuity, but that such customs
were loosely defined and flexible. His fundamental point is, therefore,
that once the traditions relating to community identity
and land rights were written down in court records and exposed to the
criteria of the invented customary model, a new unchanging body of tradition
had been created.[5] In other words, traditional
institutions were not so much destroyed as reinvented. The second difficulty arises from the presumption that natural resources
in pre-colonial societies in Africa were actually managed.
The economics of property rights tells us that communities would have
had little incentive to create rules governing the use of resources,
first, if there was a relative abundance of that resource where
supply is perfectly elastic and, second, if the costs of enforcing
exclusive use exceeded the benefits. Given the low population levels
and a relative abundance of natural resources on the southern Africa
plateau during the nineteenth century, there does not appear to be a
justification for resource conservation and the establishment of a common
property management regime. The third difficulty is that the tenets
of customary land tenure and the use of natural resources in the communal
areas do not seem to accord, even closely, with contemporary principles
of common property resource management articulated by scholars such
as Bromley (1991), Ostrom (1993) and Murphree (1991). This paper sets out initially to verify whether or not colonialism
destroyed traditional common property management institutions by examining
the traditional customs and practices of indigenous communities. It
then compares traditional practice with one fundamental contemporary
principle of resource management that characterises a common property
regime: exclusivity. In doing so, the paper tries to establish whether
traditional institutions under conditions of unprecedented increases
in human and livestock populations offer a solution for the sustainable
management of natural resources held in common and, if not, how they
could be modified so that they can. My inquiry begins, in Section 2, with an historical exposition of
customary natural resource use from pre-colonial times (1840-1890),
through the colonial period when native reserves were created, to the
emergence of post-Independence notions of traditional natural resource
management. This process of institutional change is considered in the
context of a burgeoning human and livestock population in the communal
areas. Section 3 examines the decline in the conservative conservation
narrative and the emergence of a community conservation narrative, focusing
primarily on the development of property rights theory and the principles
for designing common property regimes. I then compare the common property
rights principle of exclusivity with traditional natural resource use
practices. This difference is illustrated in Section 4 with evidence
of traditional access and harvesting practices of natural resources
in the communal areas. The differences between principle and practice
also presupposes that improvements can be made in the way natural resources
have been managed in communal areas under customary law, and equally,
that there are a set of institutional arrangements towards which change
should be directed. Section 5 takes up this discussion and suggests
new directions for research. Concluding remarks are made in the final
section about the need for historical precedence and social context
in our search for lasting solutions to the issues of poverty and resource
depletion that beset the communal areas of Zimbabwe and other countries
in southern Africa. 2. TRADITIONAL INSTITUTIONS Concepts such as tradition and community have
been widely criticized because they are loosely used to carry complex
associations of wisdom, continuity, propinquity that give
them resonance, resilience and power.[6] Nonetheless,
they remain useful concepts if their context and meaning remain clear.
Hughes (1972), for example, explains: "Just as the present colourful traditional Swazi
dress is known to have come in at the turn of the [20th] century, so
many features of the social and political organizations may well have
acquired their present form at a relatively recent date. Nonetheless,
they are specifically Swazi and traditional now." It is in this sense, therefore, that the word tradition
is used here to distinguish between what people today consider to be
their own established practices and rules governing access to land and
natural resources, as opposed to outside interventions which propose
new rules and regulations to which people are unaccustomed.[7] 2.1 PRE-COLONIAL SETTLEMENT PATTERNS Despite the difficulties presented when reconstructing pre-colonial
systems of landholding and resource use, anthropologists and historians
have combed through early documents and writings to build a reasonable
understanding of life during the pre-colonial years in central and southern
Africa.[8] For the purposes of this article, I examine
briefly the pre-colonial period between 1840 and 1890, just after the
settlement of the Ndebele in southwest Zimbabwe at Gabulawayo in 1840,
and just before the colonization of the central plateau by the British
South Africa Companys pioneer column in 1890. Early accounts of pre-colonial life in Zimbabwe indicate that the
Ndebele and Gaza off-shoots of the warrior Zulu nation
raided and extracted tribute from surrounding Shona villages for grain,
cattle and slaves. As the Shona lived in dread of these raiders, they
built their towns on hill-tops in places that were easy to defend.[9]
Scoones and Wilson (1989) maintain that the dominant farming system
of the southern Shona was based on intensive, continuous farming of
vlei areas (wetlands), the major portions of which were held by petty
warlord chiefs, and largely worked by commoners as tribute in exchange
for food and wives. In areas beyond the beyond the reach of Ndebele
influence, however, the most common form of Shona settlement was based
on shifting rather than continuous cultivation: According to traditional agricultural methods the inhabitants start
to cultivate a certain selected piece of virgin land, using the same
fields for two or three years, when they extend their reclamation for
another few years until most suitable land in the vicinity is exhausted.
Then the whole village is shifted to another area. The result has been
that villages have been moved every six to eight years or so, mainly
depending upon the amount of arable land available within easy reach.
This process met with little difficulty in the past as land was ample
and dwellings easily built.[10] By all accounts, the Shona had by 1850 built up large herds of cattle.
However, Beach (1984) describes the documentary evidence on cattle ownership
and herding only as tantalisingly vague. Descriptions by
Holleman (1952) of Shona rules governing the pasturing of cattle are
also vague and flexible: "[A] distinction was made between grazing area (ufuro) and ploughing
area (urime), in that cattle had to be grazed at a safe distance from
the cultivation area. But as there was little or no control over the
movements of villages in search of suitable arable land, cattle were
in practice allowed to graze wherever there happened to be food for
them, as long as they did not trespass upon fields under cultivation."[11] The main differences between the Shona and Ndebele settlements, lay
in the amabutho, the so-called regiments that were composed of young
Ndebele men called together into a residential unit when the king thought
fit.[12] Mathers (1891) offered the following description
of their settlements: "These kraals are posted near water, and when they have destroyed
the wood for miles around, and when there is not sufficient water or
pasture for cattle as it increases by pillage or breeding, then the
kraal is burnt and the regiment builds another in a fresh bit of country.
A large kraal or town can occupy a place for about ten years. This will
account for Inyati having removed from the place marked as such on the
older maps. Enhlangeni is the name of the place, and the Inyati regimental
kraal is now 50 miles south-east of that; while Gabulawayo is 18 miles
north of the position it occupied ten years ago."[13]
While the evidence is fragmentary, it seems probable that although
much time was spent herding cattle, especially amongst the Ndebele
that cattle were pastured around settlements: the basic rule being that
cattle should not stray into cultivated fields that had not yet been
harvested. 2.2 COMPETING COLONIAL AND NATIONALIST NARRATIVES Following the occupation of the Pioneer Column and the subjugation
of the Matabele and Mashona chiefs in the 1890s, the British South Africa
Company had by 1902 set aside native reserves solely for occupation
by Africans under traditional tribal ways. Southern Rhodesia was subsequently
divided racially into a patchwork of white commercial areas in the more
productive areas and native reserves on poorer soils: a pattern of settlement
that remains largely intact today.[14] With colonialism came dramatic changes for the indigenous people.
First, there was a boom in agriculture in the native reserves. Following
the outbreak of rinderpest in 1896 a disease that decimated cattle
throughout the country cattle numbers grew from 55,000 in 1900
to nearly a million by 1923. With the introduction of the plough, more
extensive areas could be cultivated. The indigenous population had grown
from an estimated 400,000 in 1900 to about 940,000 by 1926.[15]
As pressure began to be felt within the reserves and the first signs
of environmental degradation became evident, two narratives were being
created: the colonial administrations conservative conservation
narrative and the African nationalist narrative. The colonial conservation narrative usually pointed to the inefficient
and wasteful methods of traditional cultivation: breaking up and scratching
of the soil, broadcasting seed over an extensive area without the use
of fertilisers, and lack of crop rotation or conservation contours.
The cultivation of small and scattered patches of land required excessive
labor to keep cattle out of crops. It also meant that while pasture
around cultivated fields went to waste, areas set aside for grazing
were denuded.[16] The colonial administrations
response was to introduce the concept of centralized villages
in an attempt to improve African agricultural productivity by the use
of organic fertiliser (manure) and by confining crop cultivation to
large carefully selected and consolidated blocks of arable land, ringed
by homesteads.[17] Beyond these residential lines
lay undefined woodland and grassland, the so-called grazing areas.
In spite of these efforts, the 1938 Natural Resources Commission reported
that the result of overstocking in the Reserves and other areas
has not only been a loss of stock but also a great deterioration of
the grazing ground, much of which has already been brought to a state
where rehabilitation appears impossible.[18]
Its recommendations, embodied in the Natural Resources Act of 1941,
paved the way for more coercive conservation methods, permitting the
authorities to carry out soil protection control and compulsory destocking
to protect the environment. Still, by 1944, the Godlonton Commission
estimated that 24 reserves were more than 5% overpopulated; 19 were
50 to 100% overpopulated; and 19 were overpopulated by 100% or more.
The administration became convinced that only a major sustained effort
to improve African husbandry practices could avert rural poverty and
further ecological decline. The prevailing mood within the ranks of
the government called for a more disciplinarian approach to conservation.
This new determination found its expression in the Native Land Husbandry
Act of 1951, which was designed, firstly, to ensure that good farming
methods were practiced in the reserves and secondly, to modify the land
tenure system by giving individual title to peasant farmers. African nationalists saw the situation quite differently. Inefficient
land use and communal tenure were not the sources of declining living
standards or environmental degradation, but rather symptoms of land
hunger. The nationalists argued that growing rural populations
and livestock were hemmed in by the failure of the colonial government
to allocate them more land, land from which they had been dispossessed
and to which they had a right. According to one African nationalists
submission to a Royal Commission: The problem of the African,
the cause being this story of the peoples agony, is landlessness.[19]
As the winds of change gathered momentum during the 1950s,
the nationalists bid for independence increasingly focused on
the administrations harsh and deeply unpopular measures implemented
under the Land Husbandry Act. The Southern Rhodesian government relented
first, by abandoning the Land Husbandry Act in 1961 and second, by allocating
additional land for peasant agriculture from 29 million acres
in 1930 to 54 million acres by 1969. Although the amount of land available
for subsistence agriculture nearly doubled during this period, the African
population had more than tripled, from 1.4 million in 1930 to almost
five million in 1969. The recommendations of the Phillipss Report of 1962, which favored
a more flexible approach permitting tribal authorities to find their
own local balance between arable and grazing land, were incorporated
in the Tribal Trust Land Act of 1967.[20] In particular,
this Act restored chiefs authority to allocate land previously
denied them under the Land Husbandry Act. Achieving a balance
would prove well nigh impossible under the prevailing pressures on land.
By allowing cultivation in areas previously designated for grazing only,
it created a situation in which the burgeoning population and their
livestock had to compete for marginal and limited land resources. As
the population grew, so did the need for arable land, which meant carving
further into the already dwindling feed resources for livestock. As
more land was brought under the plough, and as the demand for additional
draught power rose, an ever increasing number of livestock had to survive
on less and less grazing land. Eventually, overstocking was considered
characteristic of most communal areas and the single most important
factor contributing to their environmental degradation.[21]
With the restoration of chiefly powers, the colonial era drew to a
close. The tenets of customary land law remained intact although reinterpreted
as the right of avail, that is: "The right held by the community as a whole, but in which every
member of that community automatically participates. From this participation
flow the rights to make what the group considers reasonable use of the
natural resources available to that community, including land."[22]
The rights flowing from this right of avail included the
right of accommodation (a place to live and an area to plough), the
right to pasture, and the right to claim a fair share to
natural resources: water, clay, minerals, wildlife and fish, forest
products, timber and firewood, etc. From the right to natural resources
flow other rights: the right of way (to move stock to and from pastures
and water) and the right to stover (to graze after fields have been
harvested). These rights, however, were only extended to a reasonable
or fair share of natural resources for subsistence purposes
only. 2.3 POST-COLONIAL TRADITION It is one of the ironies of Zimbabwean history that the Native Reserves
and other institutions created by the colonial administration - and
virulently attacked by its most ardent critics - were largely preserved
by the nationalist forces that came to power in 1980.[23]
The Tribal Trust Land Act survived largely intact after Independence,
resurfacing as the Communal Areas Act of 1982. In keeping with its nationalist
and socialist ideological roots, the new government saw the communal
areas as the arena for collective action and the embodiment of a uniquely
African socialism. Except for the provision that newly elected district
councils would become the land allocating authority in place of the
chiefs, who were considered collaborators with the former white minority
government, the Communal Areas Act of 1982 was a virtual replica of
the Tribal Trust Land Act passed by the Smith government in 1967.[24]
Even so, the notion of customary law held firm. In terms of section
8(1), the new Act specifies that the district council, when granting
consent to occupy communal land, shall have regard to customary
law relating to the allocation, occupation and use of land. The
passing of this regurgitated piece of legislation therefore saw the
seamless passage of customary tenure from the old colonial order into
a new nationalist interpretation of tradition. 2.4 AGRICULTURAL INTENSIFICATION AND INSTITUTIONAL CHANGE To what extent, therefore, have traditional institutions remained
intact or been reinvented? To start with, it would seem that Rangers
depiction of customary tenure as a colonial construct is overdrawn.
Rather, as he himself put it later, customary law does change within
the dynamics of a rural civil society by adapting to the new realities
of the colonial and post-colonial economy, but all within the rhetoric
of changelessness.[25] One of these new
realities was the resolve of the Rhodesians to improve African
agricultural methods by modifying settlement patterns and tenure. Another
was the sheer pressure of population on the land. As the population
grew, it became increasingly difficult to maintain a culture of shifting
cultivation. This land scarcity, and the colonial governments
centralization programme, brought about a more settled lifestyle, based
on continuous cultivation and, hence, increased investment in land improvements,
such as manuring and the use of inorganic fertiliser and hybrid seed.
This intensification lead, not only to what the Rukuni Report referred
to as traditional freehold, but also limitations on the
right to stover, which farmers gathered to feed their own livestock
in winter.[26] With the relentless pressure of population,
people fell back on the rhetoric of changelessness. Thousands
of landless families, and those whose soils had been exhausted, migrated
from overcrowded communal areas and settled in the less congested northern
communal areas in a large swathe that ran from Gokwe, through the mid-Zambezi
Valley, to Rushinga.[27] While these two processes agricultural intensification and
rural migration incorporated new rules into the tradition
of governing access to arable land, the right of avail to common resources
remained part of the unchanging tradition within the customary tenure
system. 3. PRINCIPLES OF COMMON PROPERTY RESOURCE MANAGEMENT Romantic European imaginings of African life had their roots in nineteenth
century explorers and missionaries such as Stanley, Livingstone, Burton,
Moffat, and Courtney Selous. This notion of Africa was poignantly captured
in the title of Mathers book, Zambesia: Englands el Dorado
in Africa, published in 1891. With colonization, the charms of Africa
were recounted by settlers and today still resonate in popular novels/films
such as I Dreamed of Africa and Out of Africa. This picture of tranquility was soon shattered by the clamor for African
independence from which an alternative image emerged, that of a suppressed
people throwing off the shackles of imperialism and colonialism: a people
searching for the roots of their own identity, history and culture.
It is from these nationalist stirrings that the concept of collective
action and the role of the community took root within development
and environmental circles in the 1960s. The following decades saw a
repudiation of the conservative narrative by discrediting Western concepts
of property rights, scientific knowledge and development.[28]
In its place, a new narrative of community conservation was created.[29]
Here, notions of ancient tribal wisdom, harmony with nature, ecological
knowledge and a pre-colonial communal existence based on subsistence
and equity held sway. Scott (1981), for example, spoke of the moral
economy and in Zimbabwe, Moyana (1984) proclaimed that the egalitarian
principles that governed the pre-colonial distribution of land ensured
peaceful operations of the customary land tenure system. Cross (writing
in South Africa) averred that the single basic principle underlying
the indigenous land systems is the commitment to the interests of society,
amounting to a deep reverence for the social good.[30]
To use one more example, Folke and Berkes claimed that indigenous knowledge
differs from scientific knowledge in being moral, ethically-based,
spiritual, intuitive, and holistic.[31] For
them, traditional ecological knowledge and management systems
developed by trial and error through millennia and handed down through
generations by cultural transmission enabled many societies to
use their resources in a way that maintained the integrity of their
local ecosystems. But a stolid piece of work and the quintessential expression of the
conservative narrative, Hardins classic paper The Tragedy of
the Commons (1968), stood in the way of the full blossoming of the
community narrative. His main argument, based on cattle grazing on common
pasture, was that individuals have a strong incentive to continually
add more cattle to the commons because they receive a benefit at no
additional cost. As a result, he hypothesized, the commons would eventually
be destroyed. The attacks on this model were rooted in the belief that
it is possible to prevent the tragedy of the commons by
designing institutions to manage natural resources, rather than changing
the tenure system itself.[32] This challenge to
Hardin has spawned a vast literature, including the theory and principles
of common property regimes. While Bromley articulated the differences
between common property regimes and open access, Ostrom collated and
elaborated on these principles in her paper, The Rudiments
of a Theory on the Origins, Survival, and Performance of Common-property
Institutions. Consensus grew that the one fundamental principle
that differentiates common property regimes from open access was exclusivity,
both in terms of boundaries and ownership. Bromley captures this principle
most succinctly: "In one important sense, then, common property has something
very much in common with private propertyexclusion of non-owners.
... The property-owning groups vary in nature, size, and internal structure
across a broad spectrum, but they are social units with definite membership
and boundaries."[33] Given that Bromley considered traditional land tenure systems to be
common property regimes, and that such regimes were characterized by
exclusivity of resource use, the expectation was that the principle
of exclusivity would be inherent in traditional systems of natural resource
management. 4. CURRENT NATURAL RESOURCE USE PATTERNS It soon became clear that these design principles sat uncomfortably
with the customary law of natural resource use. Zimbabwean scholars
therefore sought to delve deeper into the mechanisms of traditional
rules governing natural resource use in order to resolve this contradiction
and vindicate the community conservation narrative. Guveya and Chikandi (1996) selected two communal areas in Zimbabwe
Svosve in a region of high agricultural potential and Mhondoro-Ngezi
in an area of low potential in order to assess whether well-defined
rules guided grazing resource utilization. Using a stratified random
sample for their household survey, together with focus groups, their
research showed that local households were allowed to graze any number
of cattle wherever they pleased. The only restriction (rule) was to
ensure that their animals did not destroy other peoples crops.
After harvest the chief (in consultation with the headmen) declared
when farmers could graze their cattle on arable land. Even when people
were able to identify grazing areas that fell under the jurisdiction
of different traditional leaders, they felt no obligation to respect
these boundaries. This traditional right of access to the commons was also exercised
towards a formal grazing scheme that had been established by three village
development committees. Farmers in the surrounding areas cut fences
and drove their livestock into the paddocks to be grazed and watered.
They claimed to be exercising their traditional right to use this area,
arguing that no-one owns grazing as it belongs to everyone.
Even during periods of critical forage shortages, this right prevailed.
The authors therefore concluded that: "An analysis of the rules governing grazing resource use show
that in both Svosve and Mhondoro-Ngesi communal areas, there are no
boundary rules and restriction rules on the use of natural grazing.
This means access to grazing resources is open access. Thus in these
communities use of grazing resources cannot be restricted to levels
that allow for sustainable yield."[34] In the case study of Mzola state forest, the Gwaai Working Group (1997)
investigated the problem of moving cattle from the overstocked Dandara
communal area into the underutilized state forest area, which lay in
a restricted foot and mouth disease zone. Seeking a solution to this
problem, the research team decided to explore the rules and practices
of two communities (Bimba I and II) that control the use of state and
communal natural resources. They found that: In another study of five wards in the Zambezi Valley, Lynam et al.
(1997) tried to determine how households and communities use natural
resources to satisfy their needs by emphasizing the spatial pattern
of resource use. The selection of study areas was representative of
high and low agricultural potential as well as high and low population
densities. With the help of a global positioning system and aerial photography,
a team of enumerators estimated the pattern and intensity of natural
resource use from a stratified sample of twenty-four randomly selected
households at each site. This was followed by intensive discussions
with groups of local experts. The results of the study showed
that households did not observe village or ward boundaries in their
resource use or harvesting activities. On average, twenty percent of
households used resources outside their ward boundaries, and eighty-six
percent of households used resources outside their village boundaries.
They observed that where resource constraints were experienced within
a villages own boundaries, this was overcome by a spillover
use of the resources in neighbouring wards. While the authors acknowledge
that access to and use of natural resources are a result of complex
processes that are, as yet, poorly understood, they nonetheless conclude
that The boundaries of production units, as well as the controls
being applied to the use of resources within these areas, require much
clearer definition if resource use is to be sustainable. In a similar study, Mandondo (2001) assessed the clarity of resource
use boundaries and resource use access rights in five contiguous villages
in Nyaropa Ward, Nyanga (a district lying along Zimbabwes eastern
border with Mozambique). His objective was to investigate how resource
use related to village boundaries and to assess the institutional arrangements
governing the use of natural resources between villages. A participatory
rural appraisal (PRA) mapping exercise to establish the location
of natural resources in relation to village boundaries was followed
up by a formal questionnaire survey to ascertain resource use patterns.
Using a PRA matrix ranking technique, Mandondo compared peoples
access to a limited number of natural resources (fuelwood, timber, mushrooms
and wild fruit) both within and across village boundaries to determine
the degree to which these resources are subject to rules of exclusion.
His results show that although villagers depended primarily on resources
from their own villages, many of them also acquired resources from other
villages, especially wild fruits. In general, the lighter products,
such as mushrooms and wild fruits, were collected from adjoining villages,
whereas the heavier products, such as fuelwood and timber, were more
likely to be collected from within the village. The reasons had less
to do with the ownership or exclusivity of resources, and more to do
with practical considerations, such as the availability of the resource,
ease of access, the proximity of the resource, and the possibility of
accomplishing other tasks when collecting the resource. 5. DISCUSSION As their introduction makes clear, Guveya and Chikandi share in Bromleys
belief that traditional authorities ability to manage common properties
was seriously eroded by the colonial administration, thus removing the
conditions for establishing a common property rights regime. However,
tracing the rules governing use of grazing and other natural resources
from pre-colonial times to the present day reveals that the main threads
of traditional institutions have remained largely intact. Livestock
owners may graze any number of cattle anywhere (so long as they are
kept safely away from the cropping areas) and people may collect natural
resources from the most convenient locations subject to certain
rules (such as not cutting down big or fruit-bearing trees or harvesting
from sacred sites). So traditional access to resources appears deeply
etched into African culture. Both Mandondo and Lynam et al. have commented
on the general acceptance of the principle that people may collect resources
within and across village or ward boundaries, as well as the apparent
lack of acrimony when people exercise this right. This type of resource use differs significantly from the principle
of exclusivity that characterises common property regimes that Mandondo
suggests the general incongruities between administrative units and
resource use contradicts the logic of having villages exercise exclusive
legal control over resources. Instead of distinct boundaries, he argues
that it is necessary to accept soft and diffuse boundaries,
characterized by informal resource sharing, as the starting point for
community-based natural resource management. Guveya and Chikandi and
Lynam et al., on the other hand, recognize that traditional institutions
of natural resource use under the pressure of growing human and
livestock population will not be sustainable. It was for this
reason that the 1994 Land Tenure Commission recommended a programme
in accordance with principle of exclusivity to survey the communal areas,
starting with the adjudication, mapping and registration of traditional
villages in order to formalise boundaries and to formalise traditional
tenure and all subsequent transactions performed under traditional tenure.[35] These opposing positions on the principle of exclusivity are not irreconcilable.
Strong support for evolutionary institutional development and change
can be drawn from the existing literature. Central to the Boserups
(1965) now classic proposition, for example, is the idea that when land
scarcities develop as a result of population pressure, indigenous land
tenure arrangements evolve towards more individualized land rights in
response to factor price changes. This means the underlying demographic
and economic processes that induce agricultural intensification and
technical change are those which simultaneously generate a demand for
socially sanctioned institutional change in the tenure system. Whereas
initially households are allowed only to continuously cultivate land,
they are later able to bequeath and sell it. This not only creates greater
security of tenure, thereby providing incentives to make farm investments,
but it supposedly facilitates the commercialization of agriculture as
allocative efficiencies begin to emerge with a land market. Eventually,
this evolutionary process of institutional development produces a unified
system of land documentation and registration, backed up by the enforcement
of property rights.[36] We also learn from North (1990) that because rules are based on culture
they change only incrementally and marginally, persisting along a path
of institutional change over time. The challenge facing policy makers
in Zimbabwe and other southern African countries is how to modify these
deeply ingrained traditional rules and guide them along a path of evolutionary
institutional change towards a system of more sustainable natural resource
management. One promising avenue might be to intervene initially only
in those areas where population pressure, resource scarcity and agro-economic
conditions have already set in motion a process of agricultural intensification
(ie. where the community is primed for institutional change). Using
light touch facilitation techniques, communities may be
encouraged to modify their rules in order to provide incentives for
adopting patterns of behavior that lead to more sustainable resource
use. In Zimbabwe, there is already evidence that resource scarcity has
set in motion a process of institutional change. Arable land in communal
areas are being continuously cultivated and the construction of permanent
homesteads has imperceptibly changed the traditional tenurial concept
of ownership.[37] Another example is
the finding by the Gwaai Working Group (1997) that, as grazing resources
became scarce, elaborate local rules emerged to prevent grazing within
a certain area during summer in order to build up reserve pastures for
the dry winter season. These examples suggest that the pace of institutional
change may be hastened if it can be ascertained when a community is
ready to make the necessary changes. Two lines of research therefore present themselves. The first is to
undertake longitudinal retrace studies to investigate and understand
the institutional evolution of natural resource management systems.
Only when we are armed with an adequate institutional map will it be
possible to advise policy makers on the most effective strategies for
assessing when and where interventions would be most appropriate. The
second line of research is to identify those marginal changes in rules
which modify behavior towards more sustainable resource management outcomes.
Currently, however, we have little information on the effects of specific
attributes of tenure which would allow researchers to predict how changes
in tenures can modify management incentives and influence behavior that
promotes sustainable resource use. A promising way forward is to view
characteristics of tenures as representing variables within a property
rights framework, allowing researchers to compare and contrast important
features of various property right structures in systematic ways.[38]
This approach also presumes the need for carefully chosen cross-sectional
studies to find variation in key property rights characteristics that
provide insights into the representativeness of case studies (Luckert
forthcoming). For those practitioners and organizations that facilitate the emergence
of new institutions, Putnam (1993) maintains that one of the most important
lessons from his own work was the need for patience. Institutional change
requires a long term commitment by governments, donors and non-government
organizations. Another important lesson from Putnam is that the most
successful local organizations represent indigenous, participatory initiatives
in relatively cohesive local communities. With these lessons in mind,
some measure of success has been achieved in developing institutions
for community wildlife enterprises in various southern African countries.
In particular, non-government organizations working in Namibia have
provided light touch facilitation over many years that involves
working directly with communities, paying regular field visits, training
and capacity building, and monitoring the internal dynamics of power
shifts within the community. Equally important, these facilitators have
been able to provide a communication bridge between government policy
makers and donors, on the one hand, and local level organizations and
communities, on the other. As a result, legislation and policy governing
community-based wildlife conservancy management have been shaped in
accordance with design principles that characterize common property
regimes. Conservancies, for example, can only be registered after the
communal area residents themselves define the conservancy boundaries
and membership. Although this legal requirement delayed the establishment
of many conservancies, external mediators facilitated negotiations between
the various interest groups who grappled with issues, made compromises
and eventually reached a settlement based on a workable institutional
framework for common property resource management.[39]
6. CONCLUDING REMARKS By tracing the rules governing the use of natural resources (especially
grazing) this paper has shown, first, that traditional institutions
were not destroyed by colonialism or the post-colonial state, but that
they have survived largely intact. Rules have only been reinvented in
the sense that the pressure of population has resulted in resource scarcity
that has modified traditional institutions. Secondly, the paper has
shown that traditional rules do not comply with the principle of exclusivity
of common property regimes and, hence, do not in themselves offer a
lasting solution to sustainable resource use. This is especially true
under conditions of growing human and livestock densities. But more
than this, the paper has tried to show that history matters. Since,
in keeping with North (1990), institutions are path dependent
evolving by continual marginal adjustments, building upon the
preceding institutional arrangements I have proposed that traditional
institutions, as they are practiced today, are the logical starting
point from which rules could be modified step-by-step and steered towards
greater conformity with the principles of common property regimes. It
is this process by which traditional institutions could be transformed
to ensure greater sustainability in natural resource use. Fortmann (1989), in her analysis of agricultural institutions in Botswana,
criticized approaches to resource management as being ahistorical and
suggests that explanations and interpretations of existing patterns
of resource management can only be understood from a historical context.[40]
All too often, one finds African research reflecting the narratives
of European misconceptions of pre-colonial African society, colonialism
and the post-Independent state. Invariably, these lead to one-size-fits-all
policy prescriptions, the most popular at the moment being co-management
combining fragile communities with over-extended, ineffectual
and aid-dependent government departments. When policy neglects history,
culture and social context, huge amounts of effort and funding can be
wasted on misconceived initiatives, resulting in lost opportunities,
as well as frustration and fatigue. Rather, research should be founded
on a new self-confidence among African scholars, fashioned by research
competence and intellectual integrity that draws on historical precedence
to bring fresh perspectives on natural resource management into the
realm of public policy debate.
NOTES [1] Bromley 1991, 136. [2] Sithole 1997. [3] Ranger 1983 and 1993, and Cheater 1990. [4] Ranger 1983, 250. [5] Ibid, 251. [6] Adams and Hulme 2001. [7] Traditional institutions are, in other words,
informal constraints that are part of a peoples heritage that
we call culture and therefore includes values, norms, taboos and so
on (North 1990). [8] For examples, see, Holleman 1952, Beach 1980,
Ranger 1983, Cheater, 1990. [9] Mathers 1891. [10] Holleman 1952, 4. [11] Ibid, 3. [12] Beach 1984. [13] Mathers 1891,194. [14] Floyd 1972. [15] Yudelman 1964. [16] Holleman 1952 and Alvord 1958. [17] Holleman 1964, Zinyama and Whitlow 1986. [18] Quoted in Moyana 1984, 90. [19] Yudelman 1964, 83. [20] The full title of the Phillips Report was the
Development of the Economic Resources of Southern Rhodesia with Particular
Reference to the Role of African Agriculture. [21] Kay 1975. [22] Hughes 1974, 42. [23] See Arrighi 1970, Palmer and Parsons 1977,
Cliffe 1986. [24] Doré 1993. [25] Ranger 1993, 102. [26] Zimbabwe 1994 [27] Zinyama and Whitlow 1986 [28] See Bromley and Cernea 1989, Folke and Berkes
1995. [29] Hulme and Adams 2001. [30] Cross 1988, 367. [31] Folke and Berkes 1995, 125. [32] See Bromley 1991, Ostrom 1993, Hanna 1995,
Rihoy 1995. [33] Bromley 1991, 25-26. [34] Guveya and Chikandi 1996,103. [35] Land Tenure Commission 1994, 1-533. [36] See Noronha 1989, McNicoll 1990, Feder and
Feeny 1991, Doré 1994. [37] Zimbabwe 1994. [38] Luckert and Kundhlande 1997. [39] Shackleton and Campbell 2000, Jones and Murphree
2001. [40] Sithole 1997.
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