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This article was downloaded by: [Temple University Libraries]On: 21 November 2014, At: 07:12Publisher: RoutledgeInforma Ltd Registered in England and Wales Registered Number: 1072954 Registeredoffice: Mortimer House, 37-41 Mortimer Street, London W1T 3JH, UK
Development Southern AfricaPublication details, including instructions for authors andsubscription information:http://www.tandfonline.com/loi/cdsa20
Shocks and rural livelihoods in theOkavango Delta, BotswanaDonald L Kgathi , Barbara N Ngwenya & Julie WilkPublished online: 21 Jun 2007.
To cite this article: Donald L Kgathi , Barbara N Ngwenya & Julie Wilk (2007) Shocks and rurallivelihoods in the Okavango Delta, Botswana, Development Southern Africa, 24:2, 289-308, DOI:10.1080/03768350701327186
To link to this article: http://dx.doi.org/10.1080/03768350701327186
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Shocks and rural livelihoods in theOkavango Delta, Botswana
Donald L Kgathi, Barbara N Ngwenya & Julie Wilk1
This paper describes the impacts that three shocks in the Okavango Delta, Botswana, have had on
rural livelihoods: the desiccation of river channels, animal diseases, and HIV/AIDS. Primary data
was collected from five study areas, using formal questionnaire interviews and focus group discus-
sions. The paper reveals the adverse effects on rural livelihoods. It describes the way households
have been exposed to poverty and vulnerability and the various ways they have coped or adapted,
such as by re-allocating their labour, liquidating their assets to cover medical expenses and
funeral costs, reducing the area ploughed for crops, hiring labour, digging wells and switching
from flood recession agriculture to dryland farming. The Botswana government has provided
safety nets to help households cope, but this paper recommends that people’s responses to these
shocks should be taken into account in future policy and programme formulation.
1. INTRODUCTION
Households of the Okavango Delta in Botswana are prone to risk as they depend on
natural resources, which in turn depend on erratic rainfall and the variable water flow
of the Okavango River (Wolski et al., 2006). They are often adversely affected by
shocks, defined as large, unpredictable, irregular disturbances, as distinct from stresses,
which are smaller, predictable, regular and sometimes continuous (Pearce et al., 1989).
Shocks have a greater adverse effect on social, economic and environmental sustainabil-
ity than stresses, since they destroy assets (Ellis, 2000; Wisner et al., 2004).
Households’ responses to shocks include various ways of coping and adapting.
According to Ellis (2000), coping strategies are ‘short-term responses to an unplanned
crisis’ and are a form of ex post diversification. Coping strategies are not the same as
adaptive strategies, defined as long-term responses to shocks aimed at improving liveli-
hood security and poverty. According to Holzmann and Jorgensen (2000), poor
households are more vulnerable to shocks since they are more exposed and have
fewer instruments for risk management. Vulnerable households tend to be ‘defenceless’
because they are economically and socially dependent.
Knowing how households respond to shocks is of critical importance since it reveals
what the poor can do to help themselves in these circumstances. There has been only
limited research into these responses in the Okavango Delta (Kgathi et al., 2004), as is
the case with research into such responses worldwide, because they tend to be
‘ephemeral and change quickly’ and therefore ‘remain unnoticed and understudied’
1Respectively, Associate Professor, and Senior Research Fellow, Harry Oppenheimer OkavangoResearch Centre, University of Botswana; and Lecturer, Department of Water and EnvironmentalStudies, Linkoping University, Sweden. This study would not have been possible without the gen-erous financial support from the European Union (INCO-DC Programme, contract IC4-CT-2001-10040) and the University of Botswana. The authors’ special thanks also go to Professor PiersBlaikie of the University of East Anglia for critically reviewing the earlier draft of this paper,and to their colleagues at HOORC, Keta Mosepele and Monica Morrison, for reviewing thefinal draft.
Development Southern Africa Vol. 24, No. 2, June 2007
ISSN 0376-835X print/ISSN 1470-3637 online/07/020289-20# 2007 Development Bank of Southern AfricaDOI: 10.1080/03768350701327186
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(Wisner et al., 2004: 112). It is useful to understand people’s response strategies so as to
guide the formulation of interventions aimed at helping the poor.
The study described in this paper examined the impacts of shocks on rural livelihoods in
the Delta and how households respond to them. Its specific research objectives were to
(1) analyse the socio-economic impacts of shocks to rural livelihoods in the Delta;
(2) examine households’ adaptive strategies in response to these shocks; and finally
(3) determine the policy implications of the research findings.
The following section outlines the sustainable livelihoods framework, which is used as
an organising tool for the discussion. Section 3 describes the study areas and Section 4
outlines the methodology for the study. Section 5 presents the research results. Section 6
summarises the discussion and considers implications for policy.
2. THE SUSTAINABLE LIVELIHOODS FRAMEWORK
The sustainable rural livelihoods framework links the broader socio-economic com-
ponents of household assets, livelihood activities, outcomes of livelihood activities,
and factors mediating access to livelihood activities (Scoones, 1998; Ellis, 2000;
Farrington et al., 2004). According to Ellis (2000: 19), ‘a livelihood comprises the
assets (natural, physical, human, financial and social capital), the activities, and the
access to these (mediated by institutions and social relations) that together determine
the living gained by the individual or household’. Activities are strategies or various
ways in which households generate their livelihoods (Ellis, 2000). The means of securing
livelihoods are usually diversified, and can be natural resource or non-natural resource
based (Ellis, 2000). Examples of natural resource based activities in the Delta are
arable farming, livestock farming, collection of veld products, basket-making, fishing
and community based tourism. Non-natural resource based activities include formal
employment, rural trade and social protection programmes (see Figure 1; also Kgathi
et al., 2004).
Households use a combination of assets to secure livelihoods. These comprise natural,
physical, human, financial and social capital (Ellis, 2000). Different forms of livelihood
activities require access to different forms of capital in order to generate a livelihood.
Access to assets and adoption of livelihood strategies are mediated by social relations
and institutions or organisations and are also affected by trends and shocks (Ellis, 2000;
Figure 1). While institutions and social relations are factors endogenous to the household,
trends and shocks are exogenous (Ellis, 2000; Farrington et al., 2004). Scholars of the new
institutional economics define institutions as ‘rules, enforcement characteristics of rules,
and norms of behaviour that structure the repeated interaction’ (North, 1989: 1321).
Social relations are the way individuals and households are positioned in society. Such
positioning is determined by factors such as religion, class, age, ethnicity and gender
(Ellis, 2000). Trends include population change, economic growth, technological change
and change in development policies, whereas shocks include drought, diseases (of
crops, animals, and humans), pests, floods and civil war (Ellis, 2000).
According to Dercon (2001), the impacts of a shock will depend on its frequency and
intensity. Long lasting and persistent shocks make coping very difficult (Dercon,
2001), hence they have greater adverse impacts on rural livelihoods. In the Okavango
Delta, shocks include animal and human diseases, recurrent droughts and changing
flooding patterns. The flooding of the Delta, which depends on rainfall in the catchment
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area, influences access to natural capital such as land for flood recession agriculture and
water for human and animal consumption (Kgathi et al., 2005; Wolski et al., 2006).
Desiccation of river channels and flooding are common shocks in the Delta and they
result in adverse impacts on rural livelihoods. Droughts deplete assets such as natural
and financial capital, hence adversely affecting the diversification of livelihood
portfolios.
3. THE STUDY AREAS
Though this study focused on certain specific villages, the Okavango Delta – situated in
Ngamiland District in northern Botswana – was the general study area. According to the
2001 census, the population of Ngamiland was estimated at 125 000, of which 76 per
cent was based in the Delta area. This Delta, a globally renowned Ramsar site, is an
important feature of Ngamiland. It is estimated that 95 per cent of the Okavango
River water that flows into this alluvial fan is generated in the upper headwaters in
Angola. The Delta and its wetland are a great attraction for tourism, the second most
important economic activity in Botswana after diamonds (Kgathi et al., 2005). Botswana,
with a per capita income of US$3430 (2003) has one of the fastest growing economies in
Africa (World Bank, 2005), though its performance in human development has declined
since the 1990s as a result of the HIV/AIDS pandemic.
The specific study areas, situated in both the lower and upper parts of the Delta, were the
villages of Shorobe, Etsha 6, Seronga, Gudigwa and Sehitwa (Figure 2), whose main
livelihood activities are arable farming, social protection programmes, livestock
agriculture and formal employment (Kgathi et al., 2005). Table 1 shows that the 2001
population in these villages ranged from 732 in Gudigwa to 2629 in Etsha 6.
Figure 1: A framework for livelihood analysis of rural households
(Slightly adapted from Ellis (2000) for application to the Okavango Delta region):
Notes: CBNRM – Community Based Natural Resources Management; ITK –
Indigenous Technical Knowledge (ITK)
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Figure 2: Map of the Okavango Delta showing the study areas (Source: Fieldwork, 2003)
292
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4. METHODOLOGY
4.1 Data collection
The primary data was collected from the five study areas, using formal questionnaire
interviews, informal interviews and focus group discussions. The formal interview
questionnaire survey was undertaken in August, September and October 2003, after
a pre-test had been done in the village of Tubu, near the town of Gumare (Figure 2).
A detailed questionnaire, with closed and open ended questions, was used to collect
household data. Since the level of literacy in the study areas was low, individual ques-
tionnaires were administered to households face-to-face in Setswana, the national
language. The number of households interviewed in the study areas was 129, the
numbers for the individual study areas being as shown in Table 1. A two-stage stratified
random sampling method was used to select the sample. A random sample of enumer-
ations was selected, and within each enumeration area a systematic random sample was
selected using a list drawn for the 2001 Census. The sampling unit was a household,
and those interviewed were heads of households. The households were categorised
into poor, middle and rich peasants, based on the assets they held and the income
earned.
Information was also collected through six focus group discussions in the villages of
Gudigwa, Sehitwa, Shorobe and Seronga from key informants from different parts of
the village who shared similar characteristics (such as age, gender and social standing).
A set of interview instructions was used to steer the interview process and help focus
discussion on key themes. Each group discussion had a facilitator and a transcriber.
Group discussions lasted for about two hours, depending on the dynamics of the
group. The issues covered varied with the village, but were generally: 1) livelihood
activities in the village and their ranking; 2) the drying up of river channels; 3) the
killing of cattle to eradicate cattle lung disease; 4) drought; 5) damage of crops by
wildlife; and 6) HIV/AIDS.
4.2 Data analysis
The quantitative household questionnaire data was coded, cleaned up and entered for
analysis in Statistical Package for the Social Sciences (SPSS) (12.1). Analysis was in
the form of frequency distributions, measures of central tendency, and variation. In
addition, the Chi Square Test of Independence was used to test for association
between variables. Qualitative data from informal interviews, focus group discussions
and open ended questions were analysed thematically (Weiss, 1994). This involved
reduction, display and summarising of data into themes.
Table 1: Population, number of households and sample sizes in the study areas
Etsha 6 Gudigwa Sehitwa Shorobe Seronga
Population (2001) 2629 732 1478 955 1641
Number of households (2001) 580 112 416 201 364
Number of households interviewed 36 18 28 17 30
Source: CSO, 2002a.
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5. RESULTS
5.1 Overview of the patterns of livelihoods
In recent years, new livelihood activities such as social welfare schemes, tourism, sale of
veld products, and new employment opportunities have emerged in Ngamiland. The tra-
ditional livelihood activities of agriculture (both arable and livestock), fishing, and
hunting and gathering still play a significant role, but their importance has been
reduced, partly because the land they depended on (and its resources) is now used for
other activities such as tourism and conservation. There has been a marked increase in
the development of tourism in the Delta. The policies and regulations for its promotion
have curtailed access to veld products and hunting, with some increase in commercial
opportunities in craftwork, cultural tourism, tracking and guide-work. In particular,
the poor socio-economic groups have been more negatively affected by these changes
as they are more dependent on the collection of veld products and hunting (Kgathi
et al., 2004). There is therefore an increase in vulnerability to shocks in the Delta and
the rest of Ngamiland. A substantial number of households are now increasingly
relying on social protection programmes such as food rations and the old age pension,
which act as important safety nets.
Arable agriculture was ranked by 23 per cent of the households as the first most import-
ant livelihood activity (column A in Table 2). The second most important livelihood
activity in the first most important category (column A in the table) was formal employ-
ment (mainly tourism related), which was ranked by 21 per cent of the households. This
was followed by livestock farming and government protection programmes (excluding
drought relief programme), which were both ranked third by 9 per cent of the households.
However, when the ranking of the livelihood activities of the second most important cat-
egory (column B) is examined, arable agriculture still takes a lead as the most frequently
ranked livelihood activity (17 per cent of the households), followed by government pro-
tection programmes (11 per cent) and livestock farming (9 per cent).
Table 2: Livelihood activities of the Okavango Delta ranked by how households
accord importance
A B C
Livelihood activity
% of h/h ranking
livelihoods as
first n ¼ 129
% of h/h ranking
livelihoods as
second n ¼ 129
% of h/h ranking
livelihoods as
third n ¼ 129
D
Average % of a,
b, and c
Arable agriculture 23.3 17.1 7.0 15.8
Livestock farming 9.3 8.5 5.4 7.7
Formal employment 20.9 7.0 0.8 9.6
Basket making 1.6 7.0 4.7 4.4
Remittances 7.0 3.1 4.1 4.7
Government assistance 9.3 10.9 9.3 9.8
Drought relief projects 4.7 1.6 5.4 3.9
Beer brewing 3.9 10.1 1.6 5.2
Others 11.6 5.4 7.8 8.3
Note: These columns do not add up to 100% because households mentioned more than livelihood strategy.
However, the percentages are generally low because some of the households did not do the ranking of liveli-
hood activities.
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However, social protection programmes became the most frequently ranked activity
among the activities of the third most important category (column C). Livestock
farming and drought relief were ranked the third most important livelihood activities.
Although livestock farming was once the most important livelihood activity in
Ngamiland before the eradication of livestock in 1995/96, it is now significantly less
important (Fidzani et al., 1999). When the frequencies of choices in the first, second,
and third categories (columns A, B and C) are added together and averaged, arable
agriculture is still perceived to be the most important livelihood activity (16 per cent)
followed by government protection programmes (9.8 per cent) and formal employment
(9.6 per cent) (Table 2). These frequencies should be considered the most accurate as
they have been averaged from the first, second and third most important choices.
Other studies have also revealed that arable agriculture, formal employment and social
protection programmes are the most important livelihood activities in Ngamiland
(Fidzani et al., 1999). A comprehensive survey undertaken in Ngamiland in 1997
revealed that arable farming, salaries and social protection programmes were ranked
as the first most important sources of livelihood in Ngamiland by 37 per cent, 17 per
cent and 15 per cent of the households, respectively (Fidzani et al., 1999). The Every
River Has Its People (ERHIP) survey undertaken in 22 villages of the Delta revealed
that arable agriculture was the most important livelihood activity in these villages,
ranked by 39 per cent of the households as the first most important livelihood activity,
followed by formal employment, ranked by 18 per cent of the households.
5.2 Impacts of shocks and household responses
Common shocks in the Delta are animal and human diseases, recurrent droughts and
changing flood distribution patterns. Animal diseases include cattle lung disease, conta-
gious bovine pleuropneumonia (CBPP) and African animal trypanosomiasis (nagana),
and human diseases include HIV/AIDS and malaria. In Ngamiland, droughts were
experienced in the periods 1964–1965, 1982–1988 and 1995. During the 1982–1988
droughts, 28 per cent of the cattle died. Figure 3 shows that the average crop yields
Figure 3: Maize yield variations in relation to precipitation in Ngamiland (Source:Bendsen & Meyer, 2003)
Shocks and rural livelihoods in the Okavango Delta, Botswana 295
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for the period 1982–1986 were lower than 100 kg/ha. In the study areas, 73 per cent and65 per cent of the households perceived drought to be a constraint on arable and livestock
agriculture, respectively. Drought mainly affects dryland farming, which is dependent on
rainfall, but does not affect molapo farming (flood recession farming) which is more
dependent on the Okavango River floods. There are more farmers involved in dryland
farming than in molapo farming in Ngamiland. For instance, in 1997 and 1998
dryland farmers accounted for 73 per cent and 84 per cent of all the farmers, respectively,
whereas molapo farmers accounted for the remaining 27 per cent and 16 per cent,
respectively (Kgathi et al., 2005).
Crops being damaged by wildlife and livestock killed by predators were two of the main
constraints on livelihood security in the study areas. The number of cases of livestock
killings in Ngamiland ranged from 326 in 2000 to 1200 in 2003, and the cases of crop
damage from 121 in 1999 to 196 in 2003. Elephants are the main cause of crop
damage. There is a general concern that there are too many elephants in the North
West District. This is mainly attributed to the international embargo imposed by the Con-
vention on International Trade in Endangered Species (CITES) on elephant products in
local and international markets (Darkoh & Mbaiwa, 2002). The following sections
analyse in detail three particular shocks to rural livelihoods and the way households
respond to them: the desiccation of river channels, cattle lung disease (contagious
bovine pleuropneumonia), and the HIV/AIDS pandemic.
5.2.1 Desiccation of river channels
Although the Okavango River Basin is relatively pristine, a number of the Delta channels
and floodplains have dried up at various periods (Figure 4), particularly in the past 30
years. This has adversely affected the livelihoods of those who depend on river water
and the associated resources. Two reasons for the drying up of river channels have
been identified: shifts in flow distribution patterns, caused by sedimentation, and a
general decline in the inflow of the Okavango River and local rainfall observed
between the 1970s and 2000s (Wolski & Murray-Hudson, 2006). The sedimentation
process, caused by the low topographic gradient, may lead to blockages and eventually
to avulsions – ‘the diversion of a channel to a new course at a lower elevation in the
floodplain’ (McCarthy et al., 1992), a process that could also be triggered by tectonics.
The desiccation of river channels and the formation of new ones is a natural process
caused by the accumulation of sediments, resulting in the growth of vegetation that
causes blockages and avulsions. Changes in flood distribution are of two kinds,
causing two kinds of desiccation. Sedimentation makes the flow switch to another part
of the river system, causing some parts to dry up. With a reduction in inflow and local
rainfall, however, the flood water is still distributed throughout the system, but in
reduced quantities.
The Thaoge River, which used to flow to Lake Ngami, became desiccated in the 1880s
because of blockages caused by floating plant debris, leading to the formation of the
Nqoga channel in the early 1900s (McCarthy et al., 1992). The Gomoti and Santantadibe
rivers, which used to flow to the Thamalakane River, have dried up, adversely affecting
the supply of water to Shorobe village. The Santantadibe last flowed to the Thamalakane
in the 1980s, and the flow of the Gomoti has been sporadic since the 1950s. The
desiccation of these rivers is attributed partly to the blockage of the Mboroga River,
which has affected the flow of the water to the Gomoti and Santantadibe River channels
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(Bernard & Moetapele, 2003), and partly to the general decline of flood extent observed
between the 1970s and 1990s (Wolski et al., 2003).
A number of rivers and floodplains dried up in the 1970s and 1980s because of the
general decline in inflow and local rainfall: the Nhabe River, which used to flow to
Lake Ngami near the study area of Sehitwa, the floodplains that supplied the study
area of Gudigwa, and the Thaoge River that supplied the villages of Gumare, Nokaneng
and Tsau (near the study area of Etsha 6).
Figure 4: Map of the Okavango Delta showing channels and flood plains that have
dried up
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5.2.2 Impacts of desiccation
The desiccation of river channels and floodplains has adversely affected access to water
resources (for humans and livestock), molapo farming, fishing and the harvesting of veld
products in the study areas. In Shorobe and Sehitwa, the drying up of the nearby rivers
has resulted in a serious shortage of water for both humans and livestock. Edible veld
products (tsita, tswii, mokotsumo, mochaba) and others used for various purposes (for
example mokola palm, which is used for making baskets) became depleted, and can
nowadays be described as economically scarce.
Focus group discussions clearly revealed that the drying up of the river channels in
Shorobe was a disaster with more dramatic impacts than the 1996 eradication of cattle
in the area, because only a few households owned cattle and those affected were
partly compensated, whereas the desiccation of the river channels has affected everyone
and there has not been subsequent compensation for the losses.
5.2.3 Adaptive strategies
The people whose livelihoods have been affected by the drying up of the river channels
and floodplains have coped and adapted in various ways. As the river dried up, some of
the households dug wells. Others had no means to cope and adapt and no access to safety
nets, and so became poor and vulnerable. Our survey revealed the main strategies
adopted by Sehitwa households as a reaction to the drying up of the Nhabe River and
Lake Ngami, rated in the following order of importance: 1) digging wells (28 per
cent), switching from molapo farming to dryland farming (28 per cent), and depending
on the government for water supply (20 per cent) (Figure 5). It was necessary to dig wells
to provide water for humans and livestock to drink.
Figure 5: Adaptive strategies to the drying up of the river in three villages
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In Sehitwa people switched from molapo farming to dryland farming because the soils
were suitable for this, but in Shorobe the soils were generally not suitable (being
sandy and infertile) and here only 11 per cent of the households switched to dryland
farming, while the rest continued to plough their molapo fields under dry conditions.
Dryland molapo farming is a special type of dryland farming done in depressions
where run-off rainwater may collect. Social protection programmes acted as a buffer
against loss of livelihood owing to the desiccation of the rivers. In Shorobe a significant
proportion of households (43 per cent) relied on government assistance for their water
supply. In Gudigwa, 55 per cent of the households said they dug wells in response to
the drying up of the nearby floodplains; in Sehitwa only 14 per cent did this, and 5
per cent in Shorobe. The high proportion in Gudigwa could be because most of the
households there did not previously have wells as they had just been resettled.
5.2.4 Internal migration and local mobility
In addition to the above-mentioned adaptive strategies, some households out-migrated or
moved to other areas because of the desiccation: 27 per cent of the households reported
that some people had done this. The most striking movements, in the form of both
internal migration and short-term mobility, occurred in Shorobe, Sehitwa and Etsha
6. In Shorobe, 59 per cent of the households interviewed said the drying up of the
Gomoti River had acted as a push factor for some of the households to move as their
shallow wells dried up, some to a number of localities close to Shorobe (which had
water resources supplied by the government) and some to other villages such as Matsaudi
and Matlapaneng. Table 3 illustrates the impact of the drying up of the Gomoti on the
population of a number of localities near Shorobe.
The 1981–1991 inter-censual growth rates for these villages were positive, except for
Makoba. However, the growth rates for the 1991–2001 inter-censual period were nega-
tive as a result of the decrease in their population. For instance, the growth rates for the
inter-censual period 1991–1991 for Xabe, Gobomochaa and Xuxao were29.4 per cent,
22 per cent and 212.9 per cent, respectively. As a result of such migrations and local
mobility, the population of Shorobe grew by 2.3 per cent from 758 in 1991 to 955 in
2001, despite the fact that some of the Shorobe people had also out-migrated to Maun
Table 3: Trends in the population of Shorobe village and associated localities
1981 1991 2001
Population growth
rate (%): 1981–1991
Population growth
rate (%): 1991–2001
Shorobe 539 758 955 3.4 2.3
Xabe 78 126 49 4.8 29.4
Shokomokwe 86 118 79 3.2 24.0
Gobomochaa 109 89 23 2.0 213.5
Xuxau 125 252 69 7.0 212.9
Makoba 59 51 41 21.5 22.2
Mochaba 82 105 151 2.5 3.6
Source: CSO, 1982, 1992, 2002b.
Note: Population growth rates estimated by one of the authors using the exponential formula: Pn ¼ Poern, where e
is a mathematical constant with the value 2.71827, r is the population growth rate, and n is the inter-census period.
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and other places. Informal interviews revealed that those who remained in the above
localities when others out-migrated to Shorobe were mainly the poor households, as
they could not afford the costs of relocation. On the other hand, those who out-migrated
to Maun from Shorobe were mainly the economically active. This is confirmed by the
fact that the village of Shorobe’s population now has a very high proportion of people
over the age of 65 (Kgathi et al., 2004).
In Sehitwa, 54 per cent of the households reported that some people had out-migrated as
a result of the drying up of Nhabe River and Lake Ngami to a number of areas such as
Tsau, Maun, Setlatla, Maila, Naune and Dobe, where groundwater or surface water could
easily be obtained (Table 4). It was also reported that others had moved their livestock to
other areas such as Kgomotshwaana and Habu, where there was plenty of groundwater.
However, most of the respondents complained that in these areas predators were a
problem for their livestock.
Studies on rural settlement in Botswana have revealed that scarcity of water is one of the
reasons why people do not permanently settle in the lands areas (masimo) in Botswana
(Silitshena, 1982). Lack of water drives them away from the lands areas and draws them
towards the villages, where schools, health services, employment and social amenities
can be found. It is expected that this kind of movement will continue in response to
the ongoing desiccation.
5.3 Eradication of cattle lung disease
Besides the drought and the desiccation of river channels and the killing of livestock by
predators, there are other factors that constrain livestock production in the Delta, such as
animal diseases and lack of veterinary and marketing services. The livelihood survey
revealed that the majority of the households (83 per cent) saw livestock diseases as a
major constraint, followed by drought (65 per cent) and desiccation of river channels
(30 per cent). Animal diseases have adversely affected livelihoods in the past 30 years
in Ngamiland. Some of the diseases which have affected cattle are CBPP, trypanosomia-
sis and foot and mouth. For illustrative purposes, this section examines the impacts of the
eradication of CBPP on rural livelihoods in the Ngamiland, and the coping and adaptive
mechanisms adopted by households to mitigate these impacts.
5.3.1 Impacts of the killing of cattle
In an attempt to eradicate CBPP, all the 320 000 cattle in Ngamiland were killed in
1995/1996, to protect the lucrative European Union beef market, as the disease would
Table 4: Frequencies of households who said other households emigrated
Village Frequencies
Number of
households (N) % frequencies
Gudigwa 2 18 11.1
Sehitwa 15 28 53.6
Shorobe 10 17 58.8
Etsha 8 36 22.2
Source: Fieldwork.
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spread to other areas (Townsend & Segwele, 1998). Restocking took place in 1997. In
the study areas, 69 per cent of the households reported that they were among those
whose cattle were killed. There was an association between the frequencies of those
whose cattle were killed and the households’ socio-economic status, at a 5 per cent
level of significance (x2 ¼ 16.8, probability less than .0005). For instance, all the rich
households (100 per cent) said their cattle had been eradicated, as compared to 79 per
cent of the middle and 53 per cent of the poor households. According to Ndozi et al.
(1999), before the eradication of cattle in 1996, 70 per cent of the households interviewed
in Ngamiland said they owned cattle, as compared to 30 per cent after the eradication in
1999.
The government compensated farmers in cash or cattle or both, depending on their
choice (Fidzani et al., 1999). Informal interviews revealed that the majority of the house-
holds in the study areas, particularly those with small herds, received 100 per cent cash
compensation, rather than being compensated with cattle. The killing of cattle had drastic
effects on the livelihoods of the rural people in Ngamiland, the principal ones being the
loss of draught power, milk, meat and social security. The eradication of cattle also
reduced the number of people who depended on arable agriculture as a source of liveli-
hood: in 1996, before the eradication, 52 per cent of the households ranked it as their first
most important livelihood activity, compared to 37 per cent in 1997 (Fidzani et al.,
1999). This decline is attributed to a reduction in the availability of draught power
(Ndozi et al., 1999), which was mentioned as a major constraint on arable agriculture
by 41 per cent of the respondents. The lack of milk and meat because of the eradication
caused increased malnutrition in the under-fives (Fidzani et al., 1999). According to
Ndozi et al. (1999), malnutrition due to lack of protein increased from 4.2 per cent in
1995 before the eradication to 8.8 per cent in 1996, 11.3 per cent in 1997 and 8.4 per
cent, in 1998. The number of male agricultural labourers was reduced by 33 per cent
in Ngamiland from 1325 before the eradication to 884 after it, mainly because herd
boys lost their employment (Fidzani et al., 1999).
Focus group discussions and informal interviews revealed that the killing of cattle was
one of the worst shocks experienced in the past 20 years (although its effects were
less severe than those of HIV/AIDS and the desiccation of river channels in Sehitwa
and Shorobe). However, it is important to note that the direct costs of the eradication
of the disease were far lower than the accumulated costs to the economy would have
been if the disease had not been controlled (Townsend & Segwele, 1998). Eradicating
all the cattle in Ngamiland was the most realistic strategy to pursue.
5.3.2 Household coping mechanisms
The livelihood survey revealed that the coping strategies adopted to ameliorate the
effects of cattle eradication in the study areas included reducing the area of land
ploughed, resorting to donkeys as a form of draught power, switching to hoeing, and
hiring draught power. In Sehitwa, where livestock farming is an important activity,
more than 44 per cent of the households whose cattle were eradicated reported that
they had resorted to donkeys (provided by the government), despite a general concern
that donkeys are not as suitable as cattle for draught power because they are very
slow, with the result that less land is being ploughed. Other households either switched
to hoeing as a method of ploughing or gave up arable farming to engage in alternative
activities, such as formal employment and beer brewing.
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Although the government supplied the affected households with donkey draught power
and temporary food rations, most households reported that the eradication of cattle had
made them poorer and more vulnerable to poverty. They also reported that their arable
production had declined because of the lack of draught power, that they had reduced
access to meat, milk, and meat and milk products (for home consumption and sale),
and had lost their revenue from the sale of cattle.
The way the cash compensation for the killing of cattle was used made a number of
households in Ngamiland more vulnerable to poverty. Focus group discussions and
informal interviews revealed that some of the households were registered as destitute
persons after their cattle were killed, particularly those who had fewer cattle before
the eradication. This category of households also tended to be those who had obtained
100 per cent cash compensation for the eradication of their cattle. The cash was in
most cases spent rather than invested. According to Fidzani et al. (1999), 58 per cent
of households received 100 per cent cash compensation, 24 per cent received 70 per
cent, 13 per cent received 30 per cent, and 3.5 per cent did not know what type of com-
pensation they had received. Although it was a realistic strategy for the government to
eradicate all the cattle, the giving of cash compensation to some of the households
should have been avoided.
5.4 HIV/AIDS
The HIV/AIDS epidemic, an issue of major concern worldwide, poses a major threat to
households in the Delta and the rest of Botswana. Though it is a global problem, it is con-
centrated in the developing countries, particularly in sub-Saharan Africa (Cohen, 2001).
HIV/AIDS differs from other shocks because it 1) has long-term impacts, 2) attacks the
most productive cohorts, 3) puts heavy pressure on women as they play a leading role in
caring for the sick and orphans, and 4) significantly reduces the gross national product
(GNP) (Barnett & Blaikie, 1992; White & Robinson, 2000; Bayles, 2002). Shocks
such as animal diseases and the desiccation of river channels do not have such
devastating impacts on human welfare.
5.4.1 Magnitude and impacts of the epidemic
Barnett and Blaikie (1992) categorise households associated with the impacts of HIV/AIDS as ‘AIDS-affected’ or ‘AIDS-afflicted’, the former being those that are not infected
but have used their resources to support households afflicted by HIV/AIDS (support of
orphans), and the latter being households with members who are ill or have died from
HIV/AIDS. They refer to households that are neither affected nor afflicted by HIV/AIDS as ‘unaffected households’. However, this distinction was not apparent in our
study area as almost all the households had suffered from the HIV epidemic. Hence a
more useful categorisation of households would be one that indicated the level of
effect, e.g. the ‘most affected households’ or the ‘least affected households’.
The Botswana AIDS Impact Survey II of 2004 revealed that the percentage of people
who are HIV/AIDS positive was 16 per cent in Ngamiland South and 13 per cent in
Ngamiland North, as compared to the national figure of 17 per cent (CSO, 2004).
The livelihood survey revealed that 46 per cent of the households had chronically ill
members in the past year, and some of them had already died. The perceived impacts
of HIV/AIDS in the study areas included increased financial costs (46 per cent of the
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households), pressure on agricultural labour (22 per cent) and loss of employment (22 per
cent). The epidemic has negative effects on financial resources because of the costs of
transporting patients to health services, medical fees and funerals. There is pressure
on the agricultural sector because the availability of labour has been reduced owing to
the morbidity and mortality of prime age adults, and employment is lost because of
the long-term illness of some of the household members, which is particularly serious
in the case of breadwinners.
By implication, as adult mortality increases, regardless of the causes of death, so does the
possibility of surviving dependants, especially children, being displaced from estab-
lished family relations. The 2001 population census indicates that there were 40 994
orphans in Botswana, the highest incidence being in Ngamiland West, where orphans
account for 4 per cent of the total population. In the research areas, registered orphans
accounted for 4.2 per cent of the population in Gudigwa, 6.2 per cent in Etsha 6, 5.4
per cent in Sehitwa, 7.1 per cent in Seronga and 9.4 per cent in Shorobe.
Focus group discussions in Shorobe, Gudigwa and Seronga revealed that the HIV/AIDSepidemic was the most devastating shock they had ever experienced, not comparable
with other shocks in Botswana, since it resulted in illness and death. All members of
the focus group mentioned that they had experienced the death of either a household
member or a close relative. In their opinion, shocks such as drought, desiccation of
river channels and damage of crops by wildlife also had adverse effects on their liveli-
hoods, but these impacts did not compare with those of HIV/AIDS.
5.4.2 Coping and vulnerability
Focus group discussions and informal interviews revealed various ways that households
coped with HIV/AIDS in the study areas. The principal strategies included reduction in
child-bearing, intra-household re-allocation of labour, liquidating assets such as live-
stock to cover medical expenses and funeral costs, seeking the support of the extended
family and participating in burial societies.
Informal interviews in the study areas revealed that child-bearing is no longer an attrac-
tive option for women because of the risk of HIV infection. This demographic change
has partly contributed to a reduction in fertility, as confirmed by national and district
data from the 1981, 1991 and 2001 censuses. The total fertility rate (births per
woman) in Botswana dropped from 6.6 in 1981 to 4.2 in 1991 and 3.27 in 2001
(Ramolemana & Shongwe, 2003). Despite the high mortality rates of the prime age
population, the dependency ratios in Ngamiland have decreased from 124 per cent in
1991 to 83 per cent in 2001 (Majelantle, 2003). This could be attributed to low fertility
rates and the increase in infant mortality.
Besides liquidating assets and sharing labour amongst households, another strategy used
by some households was to abandon their livelihood activities when some of the house-
hold members who were actively involved in production activities became sick or died.
Informal interviews in Sehitwa and Shorobe revealed that most households either
reduced the area they ploughed or abandoned both arable and livestock agriculture
altogether. The adverse impacts on livelihood activities resulting from HIV/AIDShave marginalised and impoverished a number of households in the study areas. Accord-
ing to several respondents in our informal interviews, the most affected were female-
headed households and poor households in general.
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The extended family still plays an important role in caring for the sick and orphans in
Botswana. The focus group discussions revealed that most of the orphans in the study
areas of Seronga, Gudigwa and Shorobe were taken care of by their relatives.
This suggests that social capital is an important safety net for the afflicted households.
However, the family institution is now under great pressure as a result of the
increasing number of orphans, and the question is whether it will continue to cope
in future.
Apart from the extended family, there are social support groups, which help afflicted
households in the event of death. These include formal groups such as burial societies
and informal social groups that provide financial, social and psychological support.
Informal interviews in Shorobe and Sehitwa revealed that some of the ethnic
groups such as Herero and Batawana have burial societies and, in the event of
death, the members make financial contributions to the afflicted households, besides
providing their labour and psychological support. Relatives of the deceased also
provide financial, psychological and social support, and the level of such support nor-
mally depends on the degree of closeness to the deceased and the socio-economic
status of the provider.
6. DISCUSSION AND CONCLUSION
6.1 Summary of shocks
The drying up of the channels and flood plains has adversely affected access to water
resources (for humans and livestock), flood recession agriculture, fishing and veld pro-
ducts, and is perceived to be a worse disaster than the 1996 eradication of cattle. House-
holds have responded by digging wells, switching from flood recession to dryland
agriculture, depending on the government for water supply, and out-migrating to areas
with reliable water sources. The findings support other studies in developing countries
which reveal that out-migration is usually adopted as one of the strategies for ex post
diversification (Ellis, 2000).
Another shock, the killing of cattle in Ngamiland to eradicate CBPP, has resulted in loss
of draught power, milk, meat and social security. Households have responded by redu-
cing the area ploughed, using donkeys for draught power, and resorting to hoeing as a
method of ploughing. Government compensation of households was poorly handled:
many consumed rather than invested the cash, thus increasing their vulnerability to
poverty and destitution.
Furthermore, the HIV/AIDS pandemic has had the most devastating effects on liveli-
hoods. It has put pressure on agricultural labour as a result of the morbidity and mortality
of prime age adults, increased financial costs, and caused loss of employment. It has mar-
ginalised and impoverished a number of households in the study areas, the most affected
socio-economic groups being female-headed households and other poor peasants. The
principal coping strategies for households have included re-allocating household
labour, liquidating assets to cover medical expenses and funeral costs, seeking the
support of the extended family, participating in burial societies and enrolling in govern-
ment social welfare support programmes.
It was revealed that the impact of HIV/AIDS is significantly different from that of other
shocks since it results in illness and death, with very adverse impacts on livelihoods.
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The epidemic tended to affect the economically active population more than other
population groups, and this is likely to have adverse impacts on the economy.
6.2 Implications for interventions
The research results on the impacts of desiccation of river channels and the strategies
adopted by households to adapt to this problem could be used to construct scenarios
for assessing the possible socio-economic impacts of desiccation of river channels in
the Okavango Basin, and may be useful to researchers in other river basins for designing
similar surveys.
The outbreak of animal diseases is a worldwide problem, and other countries can draw
lessons from the Botswana experience. Although it was realistic to kill all the cattle
before the disease spread to other parts of the country in order to protect the lucrative
European Union beef market, this may be a difficult option to pursue for low-income
developing countries with limited financial resources, particularly if the costs of compen-
sation are high.
Although interventions aimed at addressing the impacts of other shocks such as the
desiccation of river channels and drought could also be useful for addressing the
impacts of HIV/AIDS, they may not necessarily be appropriate for mitigating its
impacts, owing to the distinct nature of the epidemic. Those who support the view
that general anti-poverty strategies are relevant to the mitigation of the impacts of
HIV/AIDS (White & Robinson, 2000) are ignoring the uniqueness of the impacts of
the epidemic, as revealed by this study. Policy makers need to take account of house-
holds’ responses to shocks when making policy interventions, in order not to make
wrong decisions, as the impacts of shocks are not necessarily similar.
Shocks tend to adversely affect environmental entitlements, which are important sources
of livelihoods for the rural population. It is generally known that a decline in environ-
mental entitlements further aggravates poverty and environmental degradation (Leach
et al., 1999), and although poverty is not an underlying cause of this degradation, it accel-
erates the process (Barbier, 1991). Thus, the extent to which poverty causes environ-
mental degradation depends on the options available to the poor to respond to the
problem, but usually such options are limited and consequently the poor often resort
to the overuse of natural resources (Barbier, 1991). The shocks and the subsequent
poverty may result in the degradation of the biodiversity of the Delta, particularly if
appropriate management measures are not taken.
Finally, diversification of livelihood strategies can be useful for poverty alleviation in
Ngamiland. For instance, households that depend on natural resource based activities
are more affected by drought or desiccation, whereas those that depend on non-natural
resource based activities are less affected (Kgathi et al., 2004). The sustainable
livelihood framework is therefore a useful tool for guiding interventions on poverty alle-
viation, as it also allows for the categorisation of livelihood activities and the factors
influencing them. This research will be of use in the formulation of the Delta
Management Plan, which aims at promoting the integrated sustainable management of
the Delta’s natural resources so that future generations can also derive benefits from
these resources (ODMP Secretariat, 2006). As already stated, if the socio-economic
sub-system is negatively affected by shocks, it is likely to negatively affect the bio-
physical sub-system, further reducing its ability to provide goods and services.
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