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University of Groningen

Desert Related Traditional Knowledge, Policies and Management in Wadi Allaqi, South

Eastern Desert, Egypt

Abdou Kandal, Hanaa Ali Hassan

DOI:

10.33612/diss.149297572

IMPORTANT NOTE: You are advised to consult the publisher's version (publisher's PDF) if you wish to cite from it. Please check the document version below.

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Publication date: 2020

Link to publication in University of Groningen/UMCG research database

Citation for published version (APA):

Abdou Kandal, H. A. H. (2020). Desert Related Traditional Knowledge, Policies and Management in Wadi Allaqi, South Eastern Desert, Egypt. University of Groningen. https://doi.org/10.33612/diss.149297572

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Chapter 2

Traditional knowledge (TK)

In recent years, there has been a growing, worldwide interest of scholars in traditional

knowledge (TK). According to the World Bank (1998) TK may have a role in local-level

decision-making in agriculture, health care, food preparation, education, natural-resource

management and in a host of other activities related to rural communities. Its significance

for sustainable development was stressed by the Brundtland Report, Our Common Future

(1987) and the Earth Summit in Rio de Janeiro

in 1992. The concept of TK is also

incorporated in the Agenda 21 documents of the United Nations (UNESCO 2006) and the

International Convention on Biodiversity. Several studies encourage a better

understanding of TK and its potential applicability for the goals mentioned above

(Richards, 1985; Williams and Baines, 1993; Warren et al. 1995) and they also encourage

the protection and conservation of TK (WIPO 2008; Gosart 2013). Triggered by this

recognition, increasing numbers of governments, non-governmental organizations,

international conventions and other institutions and individuals acknowledged the

potential role of TK (Harhash 2012; EEAA 2014).

2.1 Defining TK

Literature on traditional knowledge does not present a distinct definition of the concept.

This is partly due to differences in backgrounds and perspectives of the authors, to

varying degrees. Terms like traditional knowledge (TK), indigenous knowledge (IK),

traditional ecological/environmental knowledge (TEK), local knowledge (LK) and

indigenous environmental knowledge (IEK) are used interchangeably and it is difficult to

draw sharp lines between them (Sillitoe 1998; Ellen and Harris 1996). Rÿser (2011)

argues that there is sufficient overlap between the various definitions to allow for their

interchangeability, although there are distinctions to be made between them. Others find

these terms not interchangeable nor synonymous (Kudngaongarm 2009; Mugabe 1998).

Because these different terms share closely related meanings and share many attributes,

such as being unwritten, customary, pragmatic, experiential, and many times having a

holistic scope, they are regularly used in the same context. Brush (2005) attributes the

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distinction among those terms to the knowledge holders rather than to the knowledge

itself, and argues that traditional knowledge can be attributed to both indigenous peoples

and local communities. Thus, according to that perspective, traditional knowledge is a

broader category including other knowledge types or subsets, held by indigenous or local

communities. As reported by the World Intellectual Property Organization (WIPO)

traditional knowledge may have been created by any individual or group of humankind,

whether indigenous or not (WIPO 2008).

According to Acharya and Shrivastava (2008) IK, TK, TEK generally refer to “the

long-standing traditions and practices of certain regional, indigenous, or local

communities”. A similar definition is provided by Sullivan for TK, IK and LK (2016). This

author says that these terms generally refer to “knowledge systems embedded in the

cultural traditions of regional, indigenous, or local communities”. Also Makinde and

Shorunke (2013) consider IK, TK, TEK and LK as "the knowledge systems held by

traditional community that is based on their experience and adaptation to a local culture

and environment is relevant for development especially in agriculture, arts, crafts,

medicine, music, natural resources management and theatre".

However, Turnbull (2009) attributes a specific meaning to traditional knowledge,

namely a “cumulative body of knowledge and beliefs, evolving by adaptive process and

handed down through generations by cultural transmission”. On the other hand, Hansen

and Van Fleet (2013) argue that there is no clear definition of the term TK but it generally

refers to “the long-standing traditions, practices, wisdom, knowledge, and teachings of

certain indigenous communities that are usually passed on orally”. Also, the WIPO agrees

that there is no specific definition of TK, but nevertheless, this organization has defined

TK itself as "Ideas developed by traditional communities and indigenous people, in a

traditional and informal way, as a response to the needs imposed by their physical and

cultural environments” (Srinivas 2008). Likewise, in 2002, the International Council for

Science (ICSU) defined TK as “a cumulative body of knowledge, know-how, practices

and representations maintained and developed by peoples with extended histories of

interaction with the natural environment”. But additionally, the ICSU underlines a

connection with “language, naming and classification systems, resource use practices,

ritual, spirituality and worldview”.

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The definitions above have in common the accumulation of knowledge, skills and

experiences that a given society has developed and accumulated over time, based on

empirical observation and interactions with their environment and orally passed to next

generations. TK includes types of knowledge about traditional technologies of

subsistence tools and techniques for hunting, fishing, agriculture, celestial navigation,

midwifery, household economy, ethnoastronomy, ethnobotany and ecological

knowledge, traditional medicine, climate, trade and spiritual divination. They are seen as

crucial for the subsistence and improve the livelihood of local communities (Berkes 1993;

Sillitoe 2007).

According to Briggs et al. (1999) TK should be considered in a plural form and framed

as

“knowledges”: “there is a clear recognition that there is no one all-embracing

knowledge, but a range of knowledges, some perhaps better, some worse, but all relevant

to the people who hold them". These authors plea for the protection of TK as it is a central

part of identity of local communities (Briggs et al. 2007). In our view TK also encompasses

the wisdom, knowledge, and teachings of local communities and may find expression in

stories, legends, folklore, rituals, songs, laws, crafts, drawing, carving, folk music,

dancing, and sculpting. This knowledge is used to sustain the community and its culture,

as well as the biological resources necessary for the continued survival of the community

(Turner et al. 2000; Kala 2012).

2.2 Importance of TK

In the past two decades, there has been a growing global interest in traditional knowledge

systems. The Earth Summit held in Rio de Janeiro, Brazil, in 1992 for environment and

development, acknowledged the role of indigenous and local peoples and their

knowledge. TK became a topic for anthropologists, environmental researchers,

biodiversity prospectors, development experts, businessmen, decision-makers and

academics in general, and of course for local people themselves. Numerous studies on

the potentially significant role of TK have been carried out in various fields (e.g. Briggs et

al. 2007; Lwoga et al. 2010). The inclusion of voices and priorities from local communities

in scientific and management projects led to more effective development strategies

(Huntington 2000; Ahmed et al. 2003; Briggs and Sharp 2004).

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The worldwide challenge of sustainability has led to the recognition that TK needs

to be understood and incorporated into the global body of knowledge for the benefit of all

humankind (Rÿser 2012). Briggs and Sharp (2004) claimed a potential role of TK.

According to Briggs et al.

(2007) “If local environmental knowledges are to contribute

successfully to sustainable development practice in a meaningful way, it is vital that their

use in policy and planning is grounded in the economic and socio-cultural environments

in which they are found”.

As demonstrated below, TK seems to be instrumental in a way out of dilemmas in

development and can contribute to a balanced development instead of being an obstacle

for development as it was often seen formerly (Agrawal 1995). For example, DeWalt

(1994) and Pretty (1995) refer to the role and involvement of local people who by their TK

can improve the management of natural resources. Others point out the role of TK for

research aimed at improving environmental impact assessments (Brooke 1993; Inglis

1993; Stevenson 1996). The use of TK in ecological management plans and practices

can, according to Drew (2005), contribute to the improvement of conservation programs.

TK may also be useful for the understanding of ecological processes (Huntington 2000)

and thus guide biologists in ecological restoration and management systems (Nabhan

2000).

TK can also be effective as a source of socio-economic strategies for communities

facing serious environmental and health risks. Corburn (2003), Lwoga et al. (2010) and

Robinson and Wallington (2012) claim TK should be used to shape environmental policy

decisions and management solutions. According to McGregor (2004), TK can effectively

contribute to the understanding of developmental issues from the indigenous

perspectives. The latter is confirmed by the World Bank (1998) and TK is judged to be

helpful to generate complementary data in cases of management decisions with

insufficient scientific information in e.g. remote local communities (Gilchrist et al. 2005;

Chemilinsky 1991; Berkes et al. 2000). There is also growing evidence that TK can and

should play an important role in wildlife conservation, particularly in remote areas where

standard scientific approaches may be impractical (Gunn et al. 1988; Johannes 1998).

According to the 1998/99 World Development Report, knowledge, including TK, and not

capital, is the key to sustainable social and economic development (World Bank 1998).

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Traditional knowledge is, however, an underutilized resource in development

projects with regard to local communities (World Bank 2004). It also meets skepticism in

scientific communities (Pierotti and Wildcat 2000). TK studies often do not follow the

accepted hypothetico-deductivist approach of the scientific method (Gunn et al. 1988),

nor have many studies undergone independent and blind repetition of inquiry.

Approaches by local communities of managing their natural resources have often not

been tested or approved to be useful for conservation (Gadgil and Berkes 1991; Krech

1999; Hansen 2002). Moreover, as is put forward by Berkes et al. (2001) skepticism on

the potential role of TK also refers to the many forms that TK can take across cultures

and to the possible mixture of desires, perspectives and accepted scientific attitude

towards data collection and resource management.

In spite of these skeptic voices, one may postulate that TK contributes to

conservation as it is rooted in cultural habits of the local people and their collaboration in

natural resource management cannot be missed. Local communities can have a potential

role in promoting sustainable development due a strong interwovenness with economic,

social, cultural and political conditions (UN 2008; Penha-Lopes and Henfrey 2019).

2.3 The dynamics of TK

Studies like those of Agrawal (1995), Flavier et al. (1995), Ellen and Harris (1996) and

Chambers (1997) have shed light on the dynamic and constantly evolving nature of TK.

Traditional knowledge is not a fixed body of knowledge but may rather be seen as fluid

and continually influenced by reflections and experimentation in a local community as well

as by contact with external systems. TK is the consequence of practical engagement in

everyday life and constantly reinforced by experience, trial and error (Agrawal 1995;

Bebbington 1993; Briggs et al. 1999). TK is thus dynamic, provisional, evolutionary,

ever-changing and not static, (Sillitoe 1998, 2007; Kalland 2000). According to Briggs et al.

(2007): “If a particular knowledge has a value in contributing to the household economy,

it will be used and re-worked. If it has no or only limited value, it will be replaced and

subsequently forgotten”. Rapid changes and loss of TK is a reality (Springuel 2004; Briggs

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knowledge custodians, without a demonstrable plan to preserve their knowledge and

transfer it to future generations.

TK systems are influenced by modern knowledge systems that have come up with

better or more attractive alternatives, particularly the influence of modernization and the

western worldview resulting in cultural changes (Voeks and Leony 2004; Sibanda 2014).

The adaptability of TK makes it vulnerable, especially as it is transmitted orally

from generation to generation, relying on memory and therefore at risk of being lost for

future generations (Okorafor 2010). Odora Hoppers (2002) connected the erosion of TK

with an erosion of natural resources, low values being attributed to both. It is often difficult

to maintain TK as younger generations migrate to urban areas to find better life (Che Soh

and Omar 2012).

Keller et al. (2005) asserted the politics, changes in lifestyle, habitat loss and the

stigma associated with the use of traditional vegetation as food or medicine as the most

significant factors impacting TK. Briggs et al. (1993) and Springuel et al. (1997) added

the disappearance of species (as well as the appearance of some new species) as one

other factor affecting TK. Harsh environmental conditions such as drought, stress and

severe seasonal changes lead to natural habitat degradation (Chesson and Huntly 1997),

caused habitat loss and associated changes in social and economic systems (Anyinam

1995) and consequently affected TK. Introducing modern technology is a factor that can

cause serious degradation and desertification of rangelands (Upton 1995), also affecting

TK.

Of course, there have always been defenders and preservers of TK within local

communities. However, they often did not document this kind of knowledge, partly

because they were not able to do so, and notwithstanding a certain urgency to protect

own intellectual property in developing countries (Nwonwu 2008).

2.4 International perspective of TK regulation and application

The value of TK in environmental management, sustainable development, education,

health, cultural heritage, and economic development has been recognized in many

countries. Often, these countries aim to ensure that the use of TK results in social and

economic benefits to the knowledge owners (Twarog and Kapoor 2004). For example,

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countries like Nigeria (Osuide 1999), Burkina Faso (Dakuyo 2004), South Africa (Republic

of South Africa 2004), Ghana (Bodeker 2010), Cameroon (Agbor and Naidoo 2011),

China (Yongfeng 2002) and Vietnam (Anil 2004) take the value of traditional medicine in

consideration. They have developed national health care policies in such a way that

traditional health systems are incorporated into their national health policies, stimulating

research and regulating a rational use of traditional medicine.

TK also has played a role in addressing some major socio-ecological problems,

including those related to climate change, and thus have contributed to a stronger

resilience with respect to natural disturbances and hazard management, e.g. in India

(Sethi et al. 2011), Zimbabwe (Mavhura et al. 2013), Ghana (Tambo 2016) and

Switzerland (von Glasenapp and Thornton 2011). In these cases, people lived in close

contact with nature and were able to observe the conditions around them. Often, they

were the first to identify any change. TK provided them, according to these authors, with

insights, based on the traditional, ages-old practices of prediction and management of

natural disasters such as ground movements, earthquakes and floods.

TK also showed its potential to contribute to the biodiversity conservation in Ghana

(Hens 2006), Lesotho Highlands (Mokuku and Mokuku 2004), Peru (Yupari et al. 2004)

and Himalaya, India (Negi 2010), based on traditional rules owned by the local people,

which may be implemented more rigorously than governmental laws. Traditional

prohibitions of fishing and hunting as well as the recognition of ecological value of

sanctuaries are key to involve traditional knowledge and practices in biodiversity

conservation and management.

The traditional crafts of local communities have also played a role in the national

economy of some countries. For example, Panama has an extensive legal framework for

the protection of traditional crafts (Espino 2004) and India has recognized the great

economic potential of handicrafts industry for the country (Bano 2016). The role of

traditional farming systems and related craftsmanship activities e.g. local food production,

represents a sustainable example of human integration with nature in Italy (Gobattoni et

al. 2015). In addition, traditional soil taxonomy in Nigeria provides the base for agricultural

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Some countries recognize that environmental education can provide a vehicle to

incorporate TK into the school curriculum (O’Donoghue et al. 1999). South Africa's

curriculum policy mandates that both TK and environmental concerns have to be

integrated into all school-learning areas/subjects (Gopal and Sosial 2005; Le Grange

2012). The Governments of Canada (Usher 2000), Namibia (AFROL 2003) and

Bangladesh (Ahmed 2004) acknowledged TK especially in relation to natural resource

management for a more successful economy. Canada has recognized, respected and

protected the rights of indigenous communities, and has incorporated these principles

into its constitution, laws and national policies plans to ensure social and economic

benefits to the traditional knowledge owners. They offer opportunities for indigenous input

in self-government powers, control over social services such as education and health,

protected area planning, compensation payments, environmental assessment, land use

regulations, resources management and climate change, fisheries and wildlife. (Berkes

et al. 2007) and Philippines (Blanco 2000).

But there are many more countries that are working on the incorporation of TK in

their legislation, e.g. South Africa (Republic of South Africa 2004), Canada (Posey 1999)

and Peru (Tobin 2004). Other countries, e.g. Indonesia, Ethiopia and Tanzania are still

working on the development of their national based-TK policies, in order to protect and

use their TK and to make TK an effective instrument for the sustainable development.

Such a process is also essential to ensure conformity with related agreements and

conventions, where these countries do not have yet specific laws for protecting and using

TK (Irawan 2017; Allafrica no year; Shemsanga et al. 2018).

This overview of TK demonstrates an increasing recognition of TK. At the same

time, more research is needed, not only on how we can protect TK and safeguard TK for

the future, but also on how to institutionalize TK in a legal framework and to develop an

optimal way to make use of TK, not in the last place because of the global problems we

are currently facing.

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