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Perspectives on Sustainable Resource Conservation in Community Nature Reserves: A Case Study from Senegal

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The coalescing of development and conservation has recently given rise to community-based conservation. Under this framework, sustainable livelihood strategies are incorporated into conservation goals on the basis that the integration of local priorities into management guidelines benefits rather than impedes conservation efforts. Consistent with this approach, the Community Nature Reserve of Dindéfélo in Kédougou, Senegal endeavors to protect biodiversity without jeopardizing local people's reliance on natural resources. In this article we provide evidence that sustainable resource conservation is a very powerful mechanism in redirecting labor and capital away from ecosystem-degrading activities. To do this, we present three examples of projects, aiming to illustrate different ways in which local people's management and sustainable use of natural resources can be beneficial in terms of biodiversity conservation, socioeconomic development, and human well-being.
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Sustainability 2012, 4, 3158-3179; doi:10.3390/su4113158
ISSN 2071-1050
Perspectives on Sustainable Resource Conservation in
Community Nature Reserves: A Case Study from Senegal
Liliana Pacheco 1,2, Sara Fraixedas 3,*, Álvaro Fernández-Llamazares 1,3, Neus Estela 1,2,
Robert Mominee 4 and Ferran Guallar 1,2
1 Instituto Jane Goodall España (IJGE), Zoo de Barcelona, Parc de la Ciutadella, s/n,
08003 Barcelona, Spain; E-Mails: (L.P.); (A.-F.L.); (N.E.); (F.G.)
2 Réserve Naturelle Communautaire de Dindéfélo (RNCD), Dindéfélo, Kédougou, Senegal
3 Institut de Ciència i Tecnologia Ambientals (ICTA), Edifici C, Facultat de Ciències,
Campus de Bellaterra, Universitat Autònoma de Barcelona (UAB), 08193, Bellaterra
(Cerdanyola del Vallès), Spain
4 Peace Corps Senegal, B.P. 37, Kédougou (town), Lawol Bandafassi (road to Bandafassi), Senegal;
* Author to whom correspondence should be addressed; E-Mail:;
Tel.: +34-935-812-974; Fax: +34-935-813-331.
Received: 23 August 2012; in revised form: 5 November 2012 / Accepted: 6 November 2012 /
Published: 16 November 2012
Abstract: The coalescing of development and conservation has recently given rise to
community-based conservation. Under this framework, sustainable livelihood strategies are
incorporated into conservation goals on the basis that the integration of local priorities into
management guidelines benefits rather than impedes conservation efforts. Consistent with
this approach, the Community Nature Reserve of Dindéfélo in Kédougou, Senegal
endeavors to protect biodiversity without jeopardizing local people’s reliance on natural
resources. In this article we provide evidence that sustainable resource conservation is a
very powerful mechanism in redirecting labor and capital away from ecosystem-degrading
activities. To do this, we present three examples of projects, aiming to illustrate different
ways in which local people’s management and sustainable use of natural resources can
be beneficial in terms of biodiversity conservation, socioeconomic development, and
human well-being.
Sustainability 2012, 4 3159
Keywords: sustainable development; conservation strategies; community conservation;
nature reserve; Senegal
1. The Erosion of Biodiversity: Drivers and Concerns
Biodiversity erosion is currently recognized as one of the burning topics of study in the recent
scientific literature [1–3]. Since the 1970s, much research has addressed the issue with particular
emphasis on attempting to estimate the percentage of global biodiversity threatened with extinction [4–6].
The most commonly cited figure shows that up to 38% of the world’s total number of species could be
threatened with extinction [7], although it is widely recognized that this appraisal is a serious
underestimation, taking into account that biodiversity in many parts of the world, especially in tropical
latitudes, remains poorly studied and that the conservation status of only 2.7% of the world’s described
biodiversity is currently known [7,8].
Indeed, the goal of biodiversity conservation faces the complex tasks of: (1) identifying the existing
information on the ecology of species; (2) evaluating their respective causes of endangerment and
threats; and (3) establishing a conservation framework to confront their endangerment.
Extensive biological research is required for the implementation of conservation strategies and the
establishment of a protection framework for biodiversity. Until now, most of the efforts to conserve
biodiversity have come from conservationists aware of the current degradation rates of the world’s
ecosystems. However, in the last two decades some attempts have been made to try to account for local
people’s perspectives and perceptions towards biodiversity [9,10].
For most rural and indigenous people living in natural environments, forest resources are the basis
of their livelihoods, providing a wide variety of products including food, medicine, timber or charcoal,
and material for building and crafting [11,12]. Moreover, according to the World Health Organization,
up to 80% of the world’s population relies to some extent on forest resources such as medicinal plants
for curing various diseases [13], and, at the same time, these resources have an intangible spiritual
value [14,15]. Numerous studies have also revealed the importance of wild vegetal species in human
nutrition—particularly in Africa [16–18], many of which may be endangered [19–21]. It is therefore
crucial to ascertain local people’s reliance on biodiversity as a first step towards sustainable resource
conservation. This is due to two assumptions: (1) people’s well-being in many parts of the world is
highly dependent on wild resources; and (2) local people have an important role in the success of
biological conservation strategies.
2. Community Conservation and Sustainable Development
In general terms, there are two perceptions of the effects that local people’s management and use of
natural resources have in terms of biodiversity conservation. On the one hand, some authors note that
local people’s use of resources may lead to overexploitation, particularly in those cases in which there
is a regime of commercialization [22–24]. This framework provides theoretical justification for the
conservationist paradigm of strict natural protection (e.g. National Parks), where any prospection or
use of natural resources is forbidden. On the other hand, many studies argue that locals people’s
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management actually enhances biodiversity [25–27], since local knowledge-based management
strategies ensure a simultaneously focus on landscapes and species, while at the same time
specialization is avoided [28,29]. Under this framework, initiatives allowing people to live in
Community Nature Reserves to make a sustainable use of natural resources have been developed on
the basis that the incorporation of local priorities into management guidelines benefits conservation
goals [30–32]. However, as many authors hold [33,34], both views are not strictly opposed, but rather
complementary or even case specific.
The merging of development and conservation has given rise in the past few years to community-based
natural resource management. Community conservation attempts to create a link between development
and conservation [35,36], so that both may be achieved simultaneously. In this context, sustainability
emerges as a mechanism to: (1) redirect labor and capital away from activities that degrade
ecosystems; (2) encourage commercial activities supplying ecosystem services as joint outputs;
and (3) raise incomes to reduce dependence on unsustainable resource extraction. In this sense,
sustainable livelihood strategies are incorporated as substitutes to ecosystem-degrading activities [37].
This may help to close the gap between conservation managers and local communities [38,39].
This community-based approach has gained particular attention in the international conservation
arena, particularly in the sharp debate about the role of conservation in poverty reduction [33,34,40].
Disentangling the existing link between biodiversity conservation and poverty alleviation is an
important element of research in the field of conservation policy [41,42], especially in Africa where:
(1) historically, the costs of biodiversity conservation have not been distributed in proportion to their
benefits, and in many cases have been paid by local people [43–46]; and (2) there is urgent need of
poverty reduction [41]. Nowadays it is widely accepted that biodiversity crisis and poverty are related
problems that should be tackled together. However, clear conceptual frameworks are highly required if
policies in these two realms are expected to be combined [33]. In the present article it is held that
poverty reduction depends strongly on natural resource conservation. This position converges with the
approach of community-based conservation, since strictly protected areas are unlikely to achieve
poverty reduction goals [46,47].
The purpose of this paper is to examine different ways in which a coalescing between
development and conservation can be achieved in the Community Nature Reserve of Dindéfélo in
Kédougou, Senegal.
3. The Community Nature Reserve of Dindéfélo—A Study Case
3.1. Context, Data and Forest Profile
Senegal represents an ideal country in which to address the questions raised previously.
Although approximately 57.9% of Senegal’s population lives in rural areas where forest resources are
central to their livelihood [48], conservation projects including local people in their design and
implementation are still rare. Therefore, there lacks a clear understanding of the local populations’
resource use and attitudes, factors which are essential for the success of conservation projects aiming
to promote sustainable development [49,50].
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In terms of legal status, only approximately 11% of Senegal’s total land is under some form of
protection [51]. These protection figures include both natural areas managed solely under protection
objectives and nature reserves managed by local communities, such as the Community Nature Reserve
of Dindéfélo, the case study of the current article.
The Community Nature Reserve of Dindéfélo (Réserve Naturelle Communautaire de Dindéfélo,
henceforth RNCD) was created by the Rural Council of Dindéfélo in 2010 and is located in the
Kédougou Department, in the south-eastern extreme of Senegal (Figure 1). It is not only home to a
great diversity of flora and fauna, but also to great cultural variety with three ethnic groups (mainly
Fula, but also Bassari and Diakhanké) spread over 10 villages and hamlets in and around the RNCD,
giving a total sum of 6951 inhabitants and 651 households. Nevertheless, the RNCD program is
located on mostly Fula territory. Fula were known for their nomadic behavior, but in the last 50 years
they have settled in different parts of West Africa, becoming the most numerous ethnic group without
a country. Their traditional agricultural methods remain little productive and even dangerous—when
slopes are used to cultivate—and tend to extend their fields causing forest deforestation. They are also
the most prominent traders (small-scale) and shoppers of the subregion comprised from Mauritania to
Nigeria [52].
The RNCD covers an area of 13,300 ha—more than half of the total area of the Rural
Community—and it is located at the edge of two different eco-regions: the Western Sudan savannah
and the Guinean forested mosaic (eco-regions AT0707 and AT0722, respectively), according to the
classification by Olson et al. [53]. Five types of vegetation predominate in the study area:
(1) woodland, shrub and herbaceous savannah; (2) woodland; (3) dense forest; (4) gallery forest;
and (5) bowé, outcrops of laterite rock where trees and shrubs cannot grow and that are only covered
by grass during the rainy season. Land use and vegetation distribution and percentages in the RNCD
are shown in Table 1 and Figure 2.
The production system of local people is agropastoral with the primary productive activities being
agriculture, animal husbandry, and vegetable gardening. Agriculture is universally practiced amongst
the populace, with cereal grain production leading cash crops. Secondary productive activities include
the exploitation of forestry products, the transformation of agricultural commodities for local
consumption, petty commerce, fishing, artisan crafts, and some traditional gold mining [54].
Table 1. Distribution of land use in the Réserve Naturelle Communautaire de Dindéfélo (RNCD).
Type of land use Surface Area (ha) Surface Area Percentage
Woodland and herbaceous savannah 4860 37%
Forests (all types) 3197 24%
Shrub savannah 2430 18%
Bowé and prairie grass 2174 16%
Agricultural areas 512 4%
Others (houses, rocks,…) 128 1%
TOTAL 13.301 100%
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Figure 1. (a) Rural Community of Dindéfélo (Communauté Rural, CR de Dinféfélo) in the
Kédougou Department, in the south-eastern extreme of Senegal. (b) Location of the RNCD
within the Rural Community: internal zoning map in accordance with the vulnerability
criteria related to chimpanzees (Zone 1 = high level of protection; Zone 2 = medium level
of protection; Zone 3 = low level of protection).
Source: Management plan of the RNCD 2012–2016, USAID/Wula Nafaa program [55].
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Figure 2. Land use distribution in the RNCD.
Source: Management plan of the RNCD 2012-2016, USAID/Wula Nafaa program [55].
The RNCD was established with the aim of carrying out a community-based management of its
natural resources, as well as protecting the last chimpanzee population (Pan troglodytes verus) in
Senegal, listed by the International Union for the Conservation of Nature (IUCN) as a worldwide
endangered species with an estimated 500 individuals remaining in the country [56,57]. The presence
of this species in the region represents the north-western limit of its geographical distribution and the
reason why IUCN considers Dindéfélo as an important conservation area [55]. However, as in other
natural areas in Africa, the conservation of chimpanzees in the RNCD faces the impacts of local
people’s activities, which have also a significant impact on overall biodiversity and environmental
health. These mainly include deforestation, the depletion of wild edible species, fire regimes for the
creation of open pastures for cattle, and pollution of watercourses [54,58,59]. Far from being ignorant
of their role in environmental degradation, the population is well aware of the direct impacts of their
productive activities as shown by a study carried out in the region. Villagers cited hydraulic erosion,
deforestation, and wildlife disappearance as the primary natural resource management problems within
their community. Other conservation challenges cited were the frequency and intensity of bush fires,
the over-tapping of palm trees, and the degradation of water points [54]. Therefore, natural resources
in the region of Kédougou—considered one of the last bastions of wildlife in Senegal—suffer
significantly from poaching and resource overexploitation. For instance, unchecked clearing in an
attempt to confront the decline of agricultural land productivity takes part in the erosion and
degradation of biodiversity, substantially destroying some biotopes.
This collision of agendas generates a conflict of interests between local communities whose welfare
depends on the forest goods and services, and conservationists aware of the degradation of the
ecosystems. The current situation demands an extensive assessment of local sustainable biodiversity
management practices in order to address the conservation challenges of this newly established reserve
and to answer the threats menacing its ecological integrity.
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3.2. Examples of Sustainable Projects in Natural Protected Areas and Future Challenges
3.2.1. Nurseries as an Alternative to the Unsustainable Exploitation of Forest Fruits
The increasingly unsustainable exploitation of forest fruits in the RNCD is a source of degradation
and habitat fragmentation. This is exacerbated by the fact that the diet of many animals, such as the
highly endangered chimpanzee, relies on the same wild edibles collected by local communities [60].
Perhaps the most relevant example is the case of the liana Saba senegalensis (Figure 3), known also by
its Wolof name madd, the fruit of which is highly appreciated by inhabitants in south-eastern Senegal
and often appears in local markets in the dry season when crops are not available [61,62].
Recent improvements in transportation infrastructure between the capital city of Dakar and the region
of Kédougou (including the Rural Community of Dindéfélo) have opened up opportunities for the
transportation and sale of agricultural goods desired in the northern capital yet only available in the
southern regions, an example of which is the madd fruit. High northern demand couples with the
presence of useable transportation networks and the availability of common fruit stocks in the RNCD
meaning that instead of harvesting small amounts of fruit to meet local demand, RNCD residents
amass large quantities of madd in order to supply external markets [54]. It is estimated that local
people who benefit from retail or wholesale of these fruits (especially women) for final marketing in
big cities like Dakar get more than 50% of their annual income this way [63]. Increasing pressure on
the fruit, and thus the seeds contained within it, has led to a substantial decrease in the natural
regeneration of the species with subsequent negative effects on biodiversity since the chimpanzee’s
diet depends primarily on this fruit in the dry season and it serves as an endozoochorous seed dispersal
agent, improving its fertility by the passage through the intestinal tract [56,62]. Based on this, it is also
estimated that only local people draw approximately 75,000 fruits per month during the period of
greatest abundance of S. senegalensis (from May to June). This amount of fruit adds up to about
4.5 million seeds that are deliberately taken out from the forest without enabling the natural
reproduction of the liana, while an adult chimpanzee disperses a total of 426 seeds per day, feeding on
a total of 19 fruits a day [64].
In order to make the use of this resource by local communities compatible with its preservation in
the forest and its availability to chimpanzees, the viability of several courses of action has been studied
in the RNCD. Firstly, methods for collecting madd fruits are usually destructive because people often
cut down the liana, so that flowers which would bear the fruit the following year die. This is the easiest
way for people to get it, as they only have to climb up to cut the stem, without cutting each fruit
individually. In this sense, raising the population’s awareness of sustainable and non-destructive
practices can be very effective. Also, the zoning of the RNCD has allowed for the protection of certain
areas of special importance to chimpanzees, such as the gallery forests (see Zone 1 Figure 1), which
are free from any exploitation of natural resources due to their vulnerability. However, these areas are
very limited for the chimpanzees in terms of space, and this is why an alternative has been proposed by
the Jane Goodall Institute (JGI) Spain: to substitute the exploitation of wild fruits of madd in the
RNCD with small-scale community managed tree plantations. The creation of nurseries implies a
gradual reduction of the extraction of this fruit from the wild, avoiding both women collectors to
access the difficult slopes of the mountains and the conflict with chimpanzees [62].
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Figure 3. (a) Fruit of S. senegalensis; (b) S. senegalensis fruit extraction in Dindéfélo.
(a) (b)
Source: JGI Spain 2011 [54,65].
Various experiments in Senegal have demonstrated the viability of small-scale S. senegalensis
plantations. For instance, the USAID/Wula Nafaa program has developed successful experiences in the
region of Kolda, and in the Casamance region local people from Bignona have boosted their own
nursery. Thus, the proximity of the tree allows cutting the fruit in its base, so that the liana is not
damaged. The infrastructure only requires the installation of a supporting structure upon which the
liana grows. In addition to this, local people work through management committees, and only the
creation of a group responsible for the task is needed. Perhaps the main limitation of this alternative is
the time that it takes for the nursery to be productive, since S. senegalensis begins to bear fruit around
3–4 years after its plantation [65]. Therefore, it is very important during this period to raise awareness
through sensitization activities designed to promote sustainable harvest practices. In the town of
Dindéfélo, the University of Alicante and the JGI Spain have been responsible for supporting the
nursery since its creation in the summer of 2012. As for the technical assistance, volunteers of the JGI
Spain have been responsible for the training, although the collaboration of the University of Alicante,
the University Cheikh Anta Diop in Dakar, and the USAID/Wula Nafaa program have been essential
for technical issues. In early June 2012 surveys were conducted in all the villages of the RNCD, both
to collectors and trade unions (formed by a committee which manages the sale of S. senegalensis)
about the exploitation of the fruit in order to see the extraction methods, the amount of fruit extracted,
and its importance in local economy. In September 2012 S. senegalensis was transplanted to the
nursery field (see Figure 4). So far the actions that have been carried out comprise the construction of a
deep well and supporting structures and facilities for irrigation, the training of the women responsible
for the maintenance, and planting of madd seedlings. Nowadays, the Dindéfélo Women Association,
working together with the Rural Council, the JGI Spain, and the Direction des Eaux et Forets (DEF),
as well as an expert from the territory of the University Cheikh Anta Diop (UCAD) in Dakar are
handling the maintenance of the nursery (Figure 5). The main beneficiaries are women collectors
themselves, avoiding forest collection and thus improving the conservation status of chimpanzees.
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Another small-scale plantation started in summer 2012 is that of Ségou, financed by the USAID/Wula
Nafaa program [62].
Figure 4. S. senegalensis transplantation to the nursery field (September 2012).
Source: JGI Spain 2012 [62].
Figure 5. Day training and work for the maintenance of the nursery (October 2012).
Source: JGI Spain 2012 [62].
S. senegalensis is only one example of human-wildlife resources conflict as chimps and humans
share many more fruits from the forest. According to preliminary studies carried out by the JGI Spain,
at least 39 forest species representing 43% of the diet of chimpanzees are shared with the local
population [66]. Among these, eight are likely to be sold in both local and national markets:
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Lannea sp., Adansonia digitata, Detarium sp., Tamarindus indica, Parkia biglobosa, Ziziphus sp.,
Vitellaria paradoxa, Cola cordifolia [67]. Therefore, there is an urgent need to work on these species,
either by propagating them in nurseries, or if this proves impossible (as with A. digitata), by defining
operational zones for sustainable extraction and ensuring wildlife’s access to fruit.
3.2.2. Live Fencing: A Strategy for Sustainable Resource Conservation
A second sustainable project active within the RNCD is the extension of live fencing. For the
purposes of this paper, live fences are defined as “narrow linear strips of planted trees, generally
consisting of a single row of a few densely planted species that are established and managed by
farmers” [68]. Research has shown that live fencing is used throughout the world as a sustainable
agriculture practice and yields numerous benefits for local populations and the environment [69–75].
Likewise, live fencing in the RNCD contributes significantly to biodiversity and forest conservation
while, at the same time, having a positive financial impact on local people.
The primary implementer of live fencing technology within the RNCD is a cooperative project
between the NGO Trees for the Future and the U.S. Peace Corps. The aim of the project is to extend
agroforestry techniques to subsistence farmers in order to increase their food security and curb
deforestation. Data comes from a study carried out amongst participants in the larger Trees for the
Future-Peace Corps cooperative project, which involves communities in the entire region of
Kédougou. Monthly follow-up visits were performed by program extension agents during which
program participants, government officials, and prominent community leaders were interviewed
regarding aspects of the program and their agricultural and land management practices. Program staff
members in and around the RNCD and Peace Corps volunteers provide technical training and aid in
the financing of community tree nurseries that are established and maintained by local farmers to
produce saplings for the planting of live fences. Species currently being extended are Jatropha curcas,
Acacia nilotica, A. mellifera, Bauhinia rufescens and Ziziphus mauritiana. These species have been
chosen because they are effective barriers and animal deterrents, their seed is locally available, they are
fast growing, they produce income-generating by-products, and there is local demand for their use.
The Trees for the Future-Peace Corps cooperative agroforestry project has been active in the greater
Kédougou Region for four years and in the Rural Community of Dindéfélo since late 2010. Due to the
fact that a live fence takes two years to become fully effective, few complete examples exist in the
Dindéfélo Rural Community. However, numerous examples can be found in communities throughout
the Kédougou region, in Senegal, and in northern Guinea. These geographically proximate and
climatically identical examples demonstrate the effectiveness of the technology and its cultural and
environmental appropriateness.
At present, there are four participating communities—Dindéfélo, Ségou, Tiabécaré and
Yamousa—within the RNCD, as well as one additional village, Thiangué, in the Rural Community of
Dindéfélo. Until now, over 50 program participants have planted approximately 20,000 trees in live
fences, and plans are to extend the program to remaining communities within two years.
The form and function of today’s live fencing in the RNCD differs from its historic predecessors.
Traditionally, live fencing in Dindéfélo used only J. curcas and had two primary functions: the
cementing of land ownership claims and the controlling of human traffic in and out of a village for
Sustainability 2012, 4 3168
security. These practices have been documented in other areas of West Africa [73,76].
These traditional functions have largely fallen out of usage or been replaced by dead fences composed
of woven bamboo, thorny branches, and/or tree limb posts. Today, program participants cite three
main reasons for the establishment of live fences: (1) as an alternative to current fencing options for
the protection of high-value and out of season agricultural products; (2) to generate income directly
through the sale of live fencing by-products; and (3) for environmental conservation. An exploration of
these reasons will elucidate the positive impacts of live fencing within the RNCD.
Livestock free grazing is widely practiced within the RNCD and is only restricted during the period
of cereal grain production, from late-June to December. However, there are a number of profitable
agricultural products that contribute significantly to villager nutrition and dietary diversity, such as
manioc and garden vegetables, grown out of season and thus jeopardized by free grazing. In order to
protect these plants, farmers enclose them with either a dead fence or an industrial fabricated barrier
such as chain link fencings, metal posts or barbed wire. While effective, both of these fencing options
pose a number of problems that can be overcome by live fencing. Dead fences degrade within one to
two planting seasons due to aggressive termites, are labor intensive, and contribute significantly to
deforestation as wood for their construction must be gathered from wild areas in the RNCD.
Industrial fabricated barriers are financially out of reach for the majority of farmers and, being of
questionable quality and subject to harsh environmental conditions, quickly rust and deteriorate.
Alternatively, live fences, owing to the fact that they are composed of living plants, strengthen rather
than deteriorate over time, are not subject to termite damage or rust, do not require the user to cut and
gather wood, cost significantly less in terms of materials and labor than industrial barriers, and are
largely permanent once established.
An important incentive to establish a live fence is income generation from fencing by-products,
specifically the sale of J. curcas seeds and seedlings for biofuel production, artisanal soaps [77], and
Z. mauritiana “jujube” fruit for consumption [78]. These extra financial incentives—absent with dead
and industrial fencing—make J. curcas and Z. mauritiana the most popular live fencing species
amongst participants and complement conservation. Thus, by providing villagers with proximate
sources of natural products, live fencing reduces the incentive to forage for these products within the
RNCD, reducing both human traffic in wild spaces and human-wildlife competition for food sources.
Live fences fill the ubiquitous demand for durable fencing materials and reduce the need to enter
the forested spaces of the RNCD to clear cut for fence construction. Additionally, they are a means of
adding value to a field. A typical villager land management practice is to clear-cut a field, farm there
for between four and eight years, then abandon the field and begin the cycle anew. Over half of the
communities in the RNCD identified a lack of cultivatable land as an environmental issue faced by
their community. The presence of large numbers of livestock creates a need to split agricultural lands
between pasturage and production, which leads to the overexploitation of existing farmland. Instead of
allowing fallow periods or permanently abandoning depleted fields and permitting the forest and soils
to naturally regenerate, farmers stay on exhausted soils and are forced to exploit increasingly large
tracts of marginal lands in order to maintain previous production levels. These practices run contrary to
traditional land management practices, expand the human footprint on the forest, and form a vicious
cycle; as land becomes more depleted, more land must be cultivated by each farmer, causing less land
to be available to all farmers and forcing the village to expand the total acreage under cultivation.
Sustainability 2012, 4 3169
In this way, wildlife habitats are reduced and biodiversity suffers. However, the farmer who invests in
live fencing is likely to remain in his original plot and adopt traditional sustainable land use practices.
The potential gains in soil fertility in a new field are offset by the ability to cultivate out of season
crops and more tightly control planting regimens. Thus, abandoning a fully fenced-in field no longer
becomes an economically sound decision. Throughout the region of Kédougou farmers are already
practicing this technique (Figure 6).
Figure 6. Emerging live fence in the village of Ségou.
Source: Karamba Diakhaby 2011 [77,78].
Widespread adoption of live fences has the potential to preserve hectares of forest and contribute
significantly to the biodiversity within the RNCD. Research suggests that live fences provide
important supplementary habitat for birds [79,80] and other animal groups [68,81], and may act
as movement corridors across agricultural landscapes for a variety of species [68,82], including
primates [83]. While there is some risk of increasing “nuisance” wildlife incursions into farmland, the
species concerned—primarily birds and small rodents—do not cause catastrophic crop damage and
would be more than compensated for by gains resulting from the absence of the largest threat to cereal
grains, i.e. domestic animals. Live fences in the RNCD contribute to conservation not only in what
they provide in terms of habitat and movement corridors, but also in what they prevent, namely
deforestation, human traffic in wild areas and human-wildlife competition while positively benefiting
the villagers’ economic situation in a sustainable way.
3.2.3. Construction of Municipal Washing Facilities: An Example of Sustainable Policy-Making
The last sustainable project explained here is the construction of a municipal washing facility at the
village of Dindéfélo. One of the most relevant conflicts between humans and chimpanzees throughout
the RNCD concerns encounters between these great apes and other fauna and local villagers, mostly
women and young teenagers, at the water points during the dry season [55,66]. Preliminary studies in
the reserve show that locals in six out of the 10 villages in the RNCD appear to have constant conflicts
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with chimpanzees over water resources [55]. These conflicts are not a fight over the water itself, but
rather encounters involving people and wildlife attempting to access water points simultaneously.
These interactions have proven dangerous, stressful, and irritating for both sides [60].
There are several sources of water in the Rural Community of Dindéfélo. In most of the rural areas
located on the plateau, naturally occurring water holes are the only means available. These are often
located near the smaller villages, but in some cases they are as far as 2 kilometres away.
Women periodically visit the water hole in the early morning or late evening to collect water and do
the laundry. After washing, women typically leave clothes to dry on nearby branches in order to avoid
having to carry heavy loads of laundry back on their heads. Considering there is adequate water,
women will remain near water holes for some time in order to finish their laundry. This coincides with
the time when the chimpanzee and other fauna approach these points to drink [84].
Another water source in the RNCD is its many streams and rivers. These occur primarily in villages
situated on the plain, such as Dindéfélo and Ségou. Those who live near a stream of river use it for
bathing and laundry. Women regularly visit the streams throughout the day because they are often
located in gallery forests and therefore sheltered from the sun [85,86]. They immerse their soiled linens
in the running water and use large rocks to assist in the scrubbing process (see Figure 7). Chemical
washing powders and bars as well as homemade soaps are used. After scrubbing, clothes are wrung out
and left to dry in the sun or draped over bushes or branches as makeshift clothes lines [85,86].
Figure 7. Women washing clothes in the river stream of Dindéfélo.
Source: JGI Spain 2010 [85,86].
The last sources of water in the RNCD are wells. Where these are present, women pump water into
large buckets and carry it to their homes for domestic use. For families with access to wells, clothes are
washed in large basins at their homes. However, this is a relatively rare occurrence in the RNCD as
there are very few wells and those that do exist cease to have water in the dry season.
These household activities, i.e. washing clothes, dishes, and showering, as well as the fact that
streams are used as latrines and as means of human waste disposal [87] have a direct impact on water
quality, harm riverside flora, and pollute ground water (see Figure 8). Concretely, the use of water by
local people alters the physical conditions of the riverside and impacts oxygen-consuming substances
and the nutrient cycle. This entails an increase in the presence of pathogen substances dangerous for
Sustainability 2012, 4 3171
chimpanzees and other animals [60]. In addition to these factors, it is important to note the abject lack
of proper waste disposal near water sources: The plastic bags containing chemical washing powders
are left littering the riverside along with discarded clothing left hanging from the trees or on the ground
becoming a solid contaminating agent. During the dry months, when food is scarce, a small number of
these inedible clothing items are consumed by hungry livestock and primates, causing severe stomach
obstructions and sometimes resulting in death [55,60].
Figure 8. (a) Organic pollution in the washing area; (b) Clothes left drying on bushes.
(a) (b)
Source: JGI Spain 2010 [85,86].
The JGI Spain, which collaborates with the Rural Community of Dindéfélo for the execution of the
RNCD strategic management plan, designed and constructed a municipal washing facility in Dindéfélo
(Figure 9) to put an end to the increasing levels of water pollution caused by washing points in
the Reserve.
Figure 9. (a) Filter system and Moringa oleifera intensive bed; (b) Local women using the
new washing facilities.
(a) (b)
Source: JGI Spain 2012 [65,88].
Sustainability 2012, 4 3172
The infrastructure was funded by the Àrea Metropolitana de Barcelona thanks to the elaboration
and approval of the 2012–2016 RNCD’s Management Plan and was, since its outset, a collective idea
carried out with consensus of local people, particularly the approval of local women. This process was
participatory in all phases and the feedback from potential users was collected and incorporated into
the final proposal, including the location (the town center) and the favorite operating mechanism
(with taps). The selection of the village of Dindéfélo as the benefactor of the installation was justified
by two reasons: (1) it is the most populated village in the RNCD, with more than 1600 people [55];
and (2) the Dindéfélo stream used to conduct household activities situated near the highest waterfall in
Senegal, which is important for conservation and tourism, was already severely degraded by pollution
as has been recognized by the local economies. Local women were the primary benefactors of the
project, but no more so than chimpanzees and other flora and fauna of the RNCD who rely on the
stream as their water source.
The water quality in the streams of the RNCD is expected to improve in the long-term with the
construction of the washing facility, which is maintained by the same community and where users
have received the adequate training in order to minimize water pollution. This is due in large part to
the installation of a gray water waste control station consisting of a filter system and Moringa oleifera
intensive bed. The water evacuation system is simple yet effective and is comprised of several filter
layers including carbon. Following filtration, water flows into a dense plantation of M. oleifera.
This species is used by local people to purify ground water by making use of a phytoremediation
process; its roots have an essential oil that can render gray water potable [65,88]. The plant is also used
for erosion control and live fencing [88]. The installation of the washing facility solid waste
management plan focused especially on plastic bags, as well as an environmental education program in
an effort to holistically address the pollution problems faced by the Dindéfélo community. It is
important to note that the new washing facility also provides additional advantages to the users as for
instance shade or privacy, as well as alternative uses such as showering or personal hygiene.
4. Concluding Remarks
The conservation model of the RNCD began as an experiment to enhance the conservation of
African chimpanzees, which are highly endangered, from a community-based perspective. Since its
creation in 2010, it has proved that including local knowledge and people’s perceptions in the design
and implementation of management plans of Natural Protected Areas gives conservation schemes a
better chance of success. However, any management of natural resources in Community Nature
Reserves must be carried out under the framework of sustainable development. Much of the narrative
on community conservation coincides with putting the sustainable use of natural resources on top of
the strategies for achieving poverty reduction and social justice, but it generally lacks concrete
examples on how to deal with sustainability at a practical level. Although sustainable development is
always recognized as a priority for local stakeholders and conservation agents in protected areas, there
is a reduced body of literature on sustainable strategy in Natural Protected Areas and examples on how
to cope with it. In this sense, the present work is somehow unique as it provides a reliable picture of a
particular framework to develop sustainable projects that are valuable from the perspective of
biodiversity conservation. The three different examples shown in this article illustrate different paths
Sustainability 2012, 4 3173
by which conservation goals can be achieved through the sustainable use of natural resources, mainly
forest resources, improving socioeconomic development and human well-being. Small-scale
plantations of S. senegalensis avoid unsustainable harvest practices and reduce the conflict in
particular between humans and chimps during the dry season, while at the same time allowing its
preservation in the forest. Live fencing is shown as an alternative to current fencing options for the
protection of high-value and out of season agricultural products, to generate income directly through
the sale of live fencing by-products, but also contributing to conservation in terms of habitat provision
and movement corridors. Therefore, they prevent deforestation, human traffic in wild areas and
human-wildlife competition while positively benefiting the villagers’ economic situation in a
sustainable way. Finally, the municipal washing facility constructed in the village of Dindéfélo has put
an end to the increasing levels of water pollution caused by washing points in the Reserve,
ameliorating the quality of life of chimpanzees and other flora and fauna of the RNCD who rely on the
stream as their water resource. For all the reasons that have been exposed here, these projects meet the
criteria of being ecologically sustainable, economically viable and socially fair.
In a continent like Africa, where both human development and conservation of natural areas are
urgently needed, initiatives like the ones carried out in the RNCD emerge as a viable way towards
sustainable resource conservation.
This paper has benefited from discussions with Victoria Reyes-García, who has been closely
involved throughout the process of manuscript preparation. Our gratitude also goes to the Institute of
Environmental Sciences and Technology (Institut de Ciència i Tecnologia Ambientals, ICTA), and the
JGI Spain (Instituto Jane Goodall España, IJGE), for all their continued support and commitment
during the writing of this article. Special thanks also goes to the different entities and organizations
supporting the projects carried out at the RNCD: U.S. Peace Corps, Trees for the Future,
Àrea Metropolitana de Barcelona and Fundación Biodiversidad.
Conflict of Interest
The authors declare no conflict of interest.
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... We collected faecal samples in Dindefelo, located in the south-eastern part of the Kedougou region, Senegal. This area is Sudano-Guinean woodland savannah mosaic intermixed with agricultural fields [19,20]. This highly seasonal habitat has a long dry season that lasts from November to May. ...
... In this anthropogenic landscape, the chimpanzees compete with the human population for food resources [22], making this area particularly well suited for transmission dynamics studies between humans and wild chimpanzees. The water scarcity during the dry season causes humans, livestock and wildlife, including chimpanzees, to use some of the same water sources [19]. ...
... While differences in diet have been suggested as an explanation for this pattern, the reasons behind it remain unclear [77,78]; other factors, such as the ground use by the chimpanzees and their interaction with human populations, could also explain differences in B. coli prevalence between captive and wild chimpanzees [75,80]. In the present work, the chimpanzee population under study was of wild animals; however, the study area is an anthropogenic landscape with chimpanzee-human-livestock interaction in the use of food and water resources [19,22]. The negative results obtained here can be explained by either absence of the parasite in human and livestock populations of the region, which should be confirmed by studying these host species, or by the fact these chimpanzees are wild, while more consistent and intense contact between humans and chimpanzees, such as what occurs in captivity, is required for zoonotic transmission. ...
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Wild chimpanzee populations in West Africa (Pan troglodytes verus) have dramatically decreased as a direct consequence of anthropogenic activities and infectious diseases. Little information is currently available on the epidemiology, pathogenic significance, and zoonotic potential of protist species in wild chimpanzees. This study investigates the occurrence and genetic diversity of intestinal and blood protists as well as filariae in faecal samples (n = 234) from wild chimpanzees in the Dindefelo Community Nature Reserve, Senegal. PCR-based results revealed the presence of intestinal potential pathogens (Sarcocystis spp.: 11.5%; Giardia duodenalis: 2.1%; Cryptosporidium hominis: 0.9%), protist of uncertain pathogenicity (Blastocystis sp.: 5.6%), and commensal species (Entamoeba dispar: 18.4%; Troglodytella abrassarti: 5.6%). Entamoeba histolytica, Enterocytozoon bieneusi, and Balantioides coli were undetected. Blood protists including Plasmodium malariae (0.4%), Trypanosoma brucei (1.3%), and Mansonella perstans (9.8%) were also identified. Sanger sequencing analyses revealed host-adapted genetic variants within Blastocystis, but other parasitic pathogens (C. hominis, P. malariae, T. brucei, M. perstans) have zoonotic potential, suggesting that cross-species transmission between wild chimpanzees and humans is possible in areas where both species overlap. Additionally, we explored potential interactions between intestinal/blood protist species and seasonality and climate variables. Chimpanzees seem to play a more complex role on the epidemiology of pathogenic and commensal protist and nematode species than initially anticipated.
... 257,258 Like chimpanzees elsewhere, savanna populations experience habitat loss and degradation from activities such as timber and mineral extraction (Figure Box 2), charcoal production, agriculture (crops and livestock), infrastructure development, and settlement expansions or relocations. 146,[258][259][260] Little is known about crop-feeding in savanna chimpanzees. It rarely occurs in Senegal (Fongoli, 27 Heremakhono 98 ) and there are no reports of crop-feeding in Tanzania; nonetheless, it is a potential source of conflict with the people who live alongside them. ...
... In addition, savanna chimpanzees in the hottest and driest places experience competition with people and their livestock over drinking water (Dindefelo). 260 , 2 | SAVANNAS A comprehensive recognition of the abiotic and biotic components of savannas is needed to fully understand the behavior and ecology of chimpanzees living in these environments, and the utility of savanna chimpanzees to modeling hominin evolution. Notably, each ecological process (e.g., herbivory; Supporting Information) that we describe does not exclusively occur in savanna landscapes but interactions among such processes in these landscapes are in many ways biologically distinct from those of more forested areas. ...
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Chimpanzees (Pan troglodytes) are the only great apes that inhabit hot, dry, and open savannas. We review the environmental pressures of savannas on chimpanzees, such as food and water scarcity, and the evidence for chimpanzees' behavioral responses to these landscapes. In our analysis, savannas were generally associated with low chimpanzee population densities and large home ranges. In addition, thermoregulatory behaviors that likely reduce hyperthermia risk, such as cave use, were frequently observed in the hottest and driest savanna landscapes. We hypothesize that such responses are evidence of a “savanna landscape effect” in chimpanzees and offer pathways for future research to understand its evolutionary processes and mechanisms. We conclude by discussing the significance of research on savanna chimpanzees to modeling the evolution of early hominin traits and informing conservation programs for these endangered apes.
... Habituation was achieved in 2018; prior to that date scrutiny of nest site distribution and reuse, nest sites as zones of niche construction, as well as diet, contributed to the referential modeling of hominin paleo-environments (Hernandez-Aguilar et al. 2007; Moore et al. 2017; Piel et al. 2017; Stewart et al. 2011).Since the establishment of these four sites, a new fleet of research sites has continued to build on their foundation, providing a richer and broader perspective on the ecology and characteristics of chimpanzees inhabiting the "savanna end" of the ecological spectrum. The 2009 establishment of biomonitoring in the Réserve Naturelle Communautaire de Dindéfélo in Senegal(Pacheco et al. 2012, see alsoWessling et al. 2020), as well as intermittent or short-term data collection at Kharakhena (see Boyer Ontl and Pruetz, 2020); Bagnomba; Diaguiri; and Kayan, Kanoumering, Makhana, and Hérémakhono (seeWessling et al. 2020) starting in the 2010s have all enhanced our insights into this landscape. In Côte d'Ivoire, the establishment of the Comoé Chimpanzee Project in the Comoé National Park in 2014(Lapuente et al. 2020a; see alsoLapuente et al. 2020b) provides a comparison with Senegalese sites studying the life of western chimpanzees in savanna habitats. ...
... Samples were collected at the Dindefelo Community Natural Reserve, located in the Kedougou region, southeastern Senegal, about 35 km from the town of Kedougou. The vegetation of the reserve is a sudano-guinean savanna woodland [44], one of the driest and more open habitats occupied by the species [45]. All chimpanzees live in multi-female/multi-male communities composed of flexible groups that fission and fuse [46]. ...
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Abbreviata caucasica (syn. Physaloptera mordens) has been reported in human and various non-human primates including great apes. The identification of this nematode is seldom performed and relies on egg characterization at the coproscopy, in the absence of any molecular tool. Following the recovery of two adult females of A. caucasica from the feces of wild Senegalese chimpanzees, morphometric characteristics were reported and new data on the width of the esophagus (0.268-0.287 mm) and on the cuticle structure (0.70-0.122 mm) were provided. The molecular characterization of a set of mitochondrial (cox1, 16S rRNA, 12S rRNA) and nuclear (18S rRNA and ITS2) partial genes was performed. Our phylogenetic analysis indicates for the first time that A. caucasica is monophyletic with Physaloptera species. A novel molecular tool was developed for the routine diagnosis of A. caucasica and the surveillance of Nematoda infestations. An A. caucasica-specific qPCR targeting the 12S gene was assessed. The assay was able to detect up to 1.13 × 10 −3 eggs/g of fecal matter irrespective of its consistency, with an efficiency of 101.8% and a perfect adjustment (R 2 = 0.99). The infection rate by A. caucasica in the chimpanzee fecal samples was 52.08%. Only 6.19% of the environmental samples were positive for nematode DNA and any for A. caucasica. Our findings indicate the need for further studies to clarify the epidemiology, circulation, life cycle, and possible pathological effects of this infestation using the molecular tool herein developed.
... The Dindéfélo waterfall geosite is located in the DCNR which has been created with a strategic objective to contribute to alleviate poverty by creating additional revenues for local population through the promotion of an integrated, decentralized and participatory management of the natural resources of Kédougou region, in particular in the Dindéfélo commune 77 . This initiative is the result of the actions carried in 2003 by the Program Agriculture -Management of Natural Resources "Wula Nafaa" and the Department of Water and Forests of the Ministry of Environment of Senegal and USAID, in collaboration with the Jane Goodall Institute of Spain and the Biodiversidad Fundación interested in monitoring and protecting the chimpanzees that are threatened with disappearance 78,79 . ...
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The Dindéfélo Community Natural Reserve (DCNR), created to preserve the biodiversity and to ensure the sustainable development of the territory, is especially famous for its waterfalls of which the best known and the most visited is the Dindéfélo waterfall. The latter is hosted by the Neoproterozoic Dindéfélo formations in the current Kédougou region, between the Niokolo Koba National Park and the mountainous Fouta-Djalon massif in Guinea-Conakry. This latter offers a great abiotic diversity or geodiversity that consist of various rocks of differents natures and ages and geomorphological landscapes made of waterfalls, caves and plateaus, compatible with the installation of a particular biological community (biodiversity) that it is strongly threatened in Senegal and some of which are in process of disappearance. A dozen associated to the Dindéfélo waterfall geosites, which deserve to be valued and protected, have been inventoried. The Dindéfélo waterfall geosite was chosen to promote the T The GEOSITE … Cheikh Ibrahima et al... 198 geodiversity as a support of the biodiversity and the geoheritage as a tool for human and socioeconomic local sustainable development in the region. The integration of this geoheritage in the biodiversity protection and enhancement program of the DCNR and of the cultural heritage of the Bassari Country could help promoting a new touristic niche in Senegal, the geotourism and adoption of a new label, the geopark.
Antibiotic resistance genes exist naturally in various environments far from human usage. Here, we investigated multidrug-resistant Klebsiella pneumoniae, a common pathogen of chimpanzees and humans. We screened antibiotic-resistant K. pneumoniae from 48 chimpanzee stools and 38 termite mounds (N=415 samples) collected in protected areas in Senegal. The microsatellite method was used to identify chimpanzee individuals (N=13). Whole genome sequencing was performed on K. pneumoniae complex isolates to identify antibiotic-resistant genes and characterize clones. We found a high prevalence of carbapenem-resistant K. pneumoniae among chimpanzee isolates (18/48 samples from 7/13 individuals) and ceftriaxone resistance among both chimpanzee individuals (19/48) and termite mounds (7/415 termites and 3/38 termite mounds). The bla OXA-48 and the bla KPC-2 genes were carried by international pOXA-48 and pKPC-2 plasmids respectively. The ESBL plasmid carried bla CTX-M-15 , bla TEM-1B and bla OXA-1 genes. Genome sequencing of 56 isolates identified two major clones associated with hospital-acquired infections of K. pneumoniae (ST307 and ST147) in chimpanzees and termites, suggesting circulation of strains between the two species, as chimpanzees feed on termites. The source and selection pressure of these clones in this environment need to be explored.
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Fighting against vector-borne diseases (VBD) relies essentially on the control of three main links: (i) the pathogen itself, (ii) the hosts (vectors and definitive hosts) and (iii) their interactions within their ecosystem. The present thesis inductively studies, on the one hand, the paradigm controls of VBD (mainly helminthiasis) of animals and on the other hand the role of sentinel animals in the transmission of VBD. We have studied the bacteria of the genus Wolbachia, an arthropod and filarial associated-endosymbiotic, often used for the control of VBD. The cell coculture system using Drosophila S2 cells allowed us to characterise the genome of Wolbachia massiliensis sp. nov. (wChem), a type strain of a new supergroup T. The bacteria were isolated from Cimex hemipterus collected in Senegal. The taxo-genomic study made it possible to distinguish clearly this new species from all other Wolbachia, as well as the need to review the taxonomy of this bacterial genus. Analysis of the W. massiliensis genome and its metabolic pathways show a profile close to that of the mutualistic Wolbachia of the human lymphatic filaria (Brugia malayi), which offers a new insight for deepening our knowledge of this symbiotic relationship. On the other hand, the involvement of Wolbachia as a molecular target for the diagnosis of canine filariasis has improved the detection of the occult form of these infections. However, we have proposed new molecular diagnosis approach based primarily on TaqMan® technology, combining multiple detection by qPCR, both of filaria as well as their Wolbachia. The main target species are those found in the Mediterranean basin, namely Dirofilaria immitis, D. repens, Acanthocheilonema reconditum, Cercopithifilaria grassii, C. bainae and Cercopithifilaria sp. II. In the second part of the present work, we characterized molecularly and/or morphologically nematodes of non-human primates (PNHs) from both the New and the Old World. Our results show that at least eleven species of gastrointestinal nematodes, often with zoonotic concern, have been characterized from faeces of African PNHs. Among them, Abbreviata caucasica, a parasite for which we have provided morphological data and a new specific molecular tool for its diagnosis and epidemiological surveillance. We also provided preliminary data on previously unidentified filarial parasites in neotropics monkeys (howler monkeys) of French Guiana, where at least three genotypes were identified. One of them belongs to the genus Brugia, a potential zoonosis. In addition, we have proposed a molecular detection system (qPCR) specific to this genus, in order to better diagnose, monitor and understand the life cycle of this parasite. In terms of protection against canine vector-borne diseases (CVBD), we evaluated in the field, the effectiveness of the multimodal monthly prophylactic strategy, based on the use of two products (Vectra® 3D associated with Milbactor®) against dirofilarioses, leishmaniasis (LCan) and ehrlichiosis. We therefore assessed the efficacy of artesunate in the treatment of LCan using a non-inferiority trial. In the context of biological pest control, an amine produced by the bacterial strain Serratia marcescens P400 has been partially characterized, which has been proven an insecticidal effect higher than that of ivermectin in keeling Aedes albopictus larvae. A natural infection of ticks with by parasite entomophagus wasps has also been detected. These data may offer an excellent alternative for biological control of these vectors. Finally, we demonstrated the role played by sentinel animals in the transmission and spread of VBD. Thus, the canine host, particularly dogs in Guyana, in metropolitan France, in Algeria and in Côte d'Ivoire, have a sentinel role for the maintenance and spread of BVD (dirofilariosis, leishmaniosis and trypanosomiasis). We also demonstrated the sentinel role in Italy for Rickettsiales played by reptiles. Moreover gorillas, in the Republic of Congo, have a sentinel role for gastrointestinal zoonoses (Giardia lamblia, Necator americanus, Ascaris lumbricoides, Strongyloides stercoralis and several unidentified nematodes). Finally, my thesis shows it is useful to develop and adapt new strategies for the control and surveillance of vector-borne diseases. I modestly contribute to make up for the lack of implementation of efficient techniques and knowledge in the perspective of a complete paradigm for the study of VBD in their ecosystem.
Globally, continuing environmental degradation is leading many countries to strengthen their systems of protected areas. However, this may not be sufficient to halt degradation and conserve biodiversity and ecosystem services. To supplement its growing system of protected areas, the Chinese government is adopting a strategy of Ecological Conservation Redlines (ECRs). The ECRs define limits to human encroachment into ecologically sensitive and vulnerable areas and enforce strict conservation in order to guarantee national ecological security. ECRs are integrated in their design, are based on sound science, and provide a systemic management mechanism. ECR supports the formation of a comprehensive ecological conservation system that will lead to effective conservation for the most ecologically valuable and fragile ecosystems. The ECR approach seeks to improve China’s ecological security and guide nature conservation in the future. It could also provide a valuable example of an effective approach for improving nature conservation worldwide.
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With the overall trends of deterioration in resources and ecological environments not being completely reversed, the Chinese government has adopted the strategy of establishing the Ecological Conservation Redline (ECR). The ECR aims to define limits to the encroachment onto protected ecologically vulnerable and sensitive areas, to prohibit development in these areas, and to enforce strict protection to guarantee regional ecological security. Climate data, remote sensing data, and other related data were used to identify an ECR in Heze, thereby providing an example of principle and methodology for ECR delimitation. After assessment, comprehensive treatment, and coordination analysis, a total area of 924.17 km2, accounting for 7.55% of the city’s total area, was identified as an ECR in Heze. This mainly comprised the area around the Yellow River, the old course of the Yellow River, and the Dongyu River.
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Community-based conservation (CBC) institutions are widely regarded as transformative bodies that benefit social and ecological processes in coupled social-ecological systems. Yet, limited empirical evidence for this claim exists, especially on the African continent where community-based conservancies (CBCs) are being rapidly adopted in diverse institutional forms across multiple countries. We provide the first large-scale systematic review of CBC outcomes in sub-Saharan Africa. We review the literature on CBCs and develop a conceptual model that illustrates the nested scales of interaction in which CBCs are embedded, the institutional processes (“conditions”) reported as important for success, and the outcomes of CBCs on social and ecological systems. The mixed-method approach consists of inductive/deductive textual analysis of cases, geospatial visualization, descriptive statistics, and correlational analysis. Results indicate that more often than not, establishment of CBCs in Africa has led to negative or a mixture of positive and negative social outcomes, whereas ecological outcomes have been largely positive. The research conducted on CBC institutions has overwhelmingly focused on social outcomes, using qualitative methods. Monetary and nonmonetary incentives seem to be important but not sufficient on their own for positive outcomes. Devolution of rights to the local community is significantly associated with CBC outcomes but was not present in many cases, despite this feature being a hallmark of CBCs. A number of conditions were not reported in the cases reviewed, including leadership, social learning, consideration of cultural worldviews, and diverse partnerships. We provide indepth examples of the types and diversity of outcomes and contexts underpinning the presence or absence of societal processes, highlight important gaps in the existing research, and offer guidelines for research and evaluation moving forward.
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Shifting cultivation systems, one of the most widely distributed forms of agriculture in the tropics, provide not only crops of cultural significance, but also medicinal, edible, ritual, fuel, and forage resources, which contribute to the livelihoods, health, and cultural identity of local people. In many regions across the globe, shifting cultivation systems are undergoing important changes, one of the most pervasive being a shortening of the fallow cycle. Although there has been much attention drawn to declines in crop yields in conjunction with reductions in fallow times, little if any research has focused on the dynamics of noncrop plant resources. In this paper, we use a data set of 26 fields of the same age, i.e., similar to 1.5 yr, but differing in the length and frequency of past fallow cycles, to examine the impact of shorter fallow periods on the availability of noncrop plant resources. The resources examined are collected in shifting cultivation fields by the Yucatec Maya in Quintana Roo, Mexico. These included firewood, which is cut from remnant trees and stumps spared at the time of felling, and 17 forage species that form part of the weed vegetation. Firewood showed an overall decrease in basal area with shorter fallow cycles, which was mostly related to the smaller diameter of the spared stumps and trees in short-fallow milpas. In contrast, forage species showed a mixed response. Species increasing in abundance in short-fallow milpas tended to be short-lived herbs and shrubs often with weedy habits, whereas those declining in abundance were predominantly pioneer trees and animal-dispersed species. Coppicing tree species showed a neutral response to fallow intensity. Within the cultural and ecological context of our study area, we expect that declines in firewood availability will be most significant for livelihoods because of the high reliance on firewood for local fuel needs and the fact that the main alternative source of firewood, forest patches, has also declined in short-fallow areas. Declines in some forage species can likely be compensated for by the use of other species or by adaptive responses such as managing declining species in home gardens. However, the loss of pioneer tree species in short-fallow milpas suggests that the regenerative capacity of the fallows may be reduced with implications for maintaining effective fallow cycles in this shifting cultivation system. Our findings indicate that the dynamics of noncrop plant resources and their implications for local livelihoods require further consideration in the debate over improving the productivity of shifting cultivation systems.
Live fences may act as tools for biodiversity conservation by providing habitat for native species and increasing connectivity in the landscape. We studied the influence of live fence characteristics on species richness and fence use by birds by examining both local and landscape factors. We studied three types of live fences: planted fences of a native tree, planted fences of an exotic, and spontaneous. They were either connected to forest fragments or isolated, and were all within a pasture matrix. Spontaneous and planted live fences maintain a diverse plant (77 shrub and tree species) and bird communities (98 species). Fence types strongly differed in vegetation composition and structure. We found that by analyzing each fence characteristic independently, there was no difference in bird richness or abundance. However, there was a significant correlation when plant richness, structure, and connectivity were analyzed together. This could be the result of some variables counterbalancing each other. Birds used fences for a variety of purposes including foraging, breeding, and moving across the landscape. Native birds and plants used live fences as habitat and refuge in a landscape where large forest tracts have been lost for decades. Live fences in conjunction with small forest fragments maintain a diverse array of plant and birds species that are a subsample of the species originally found in the landscape before extensive deforestation. We recommend the establishment of live fences, allowing growth of spontaneous understory.
The progressive desertification in many semiarid regions of the world increases the need for plants that can cope with arid environments and meet peoples’ requirements for food, fodder and fuel. Species of fruit trees in the genus Ziziphus represent examples of such multipurpose plants with great potential for selection and use in drought-prone regions. Ziziphus trees and shrubs inhabit arid environments on every continent due to their versatility in being able to adapt to drought stress. They play an important role in the conservation of soil, with their strong root system which stabilizes the soil and protects it from erosion. The leaves provide fodder for livestock, the hard wood is used for turning, making agricultural implements, fuel and high quality charcoal. In many regions, Ziziphus is grown as a hedge, with its spines creating effective live-fencing, and with its highly nutritious fruits providing a valuable source of energy, vitamins and also income when sold on local markets. In addition, extracts from fruits, seeds, leaves, roots and bark of Ziziphus trees are used in many traditional medicines to alleviate the effects of insomnia, skin diseases, inflammatory conditions and fever. For these reasons, Ziziphus trees have an important role to play in the integrated economy of the arid lands.