- January 2003
- In book: Wetlands of Ethiopia (pp.67-75)
- Edition: 1st
- Chapter: 8
- Publisher: IUCN – The World Conservation Union
- Editors: Yilma D. Abebe and Kim Geheb
Authors:
Figures
Map of Ethiopia showing the regions and positions of neighbouring countries
Broad strategies used in the National Wetlands Programme to improve wetland management in Uganda
. Details of the core wetland sites where biodiversity monitoring was undertaken
No caption available
…
Figures – uploaded by Zerihun Desta Beshah
Author content
Content may be subject to copyright.
Discover the world’s research
- 20+ million members
- 135+ million publications
- 700k+ research projects
Public Full-text 1
Content uploaded by Zerihun Desta Beshah
Author content
Content may be subject to copyright.
Wetlands of Ethiopia
Proceedings of a seminar on the resources and
status of in Ethiopia’s wetlands
Yilma D. Abebe and Kim Geheb(Editors)
IUCN – The World Conservation Union
Founded in 1948, The World Conservation Union brings together States,
government agencies and a diverse range of non-governmental organisations
in a unique world partnership: over 980 members in all, spread across some
140 countries.
As a Union, IUCN seeks to influence, encourage and assist societies
throughout the world to conserve the integrity and diversity of nature and to
ensure that any use of natural resources is equitable and ecologically
sustainable.
The World Conservation Union builds on the strengths of its members,
networks and partners to enhance their capacity and to support global
alliances to safeguard natural resources at local, regional and global levels.
IUCN Wetlands and WaterResources
Programme
Rue Mauverney 28
CH-1196 Gland, Switzerland
Tel: + 41 22 999 0001
Fax: + 41 22 999 0002
E-mail:[email protected]
www.iucn.org/themes/wetlands/
IUCN Eastern Africa
Regional Office
P. O. Box 68200-00200
Nairobi, Kenya
Tel: ++ 254 20 890605-12
Fax: ++ 254 20 890615/407
E-mail: [email protected]
IUCN
Wetlands
and Water
Resources
Programme
IUCN
Wetlands of Ethiopia
BLUE SERIES
Wetlands of Ethiopia
Proceedings of a seminar on the resources and
status of Ethiopia’s wetlands
Editors
Yilma D. Abebe and Kim Geheb
IUCN
2003
Published by: IUCN
Copyright: 2003. International Union for Conservation of Nature and Natural
Resources
This publication may be produced in whole or part and in any form
for education or non-profit uses, without special permission from the
copyright holder, provided acknowledgement of the source is made.
IUCN would appreciate receiving a copy of any publication which
uses this publication as a source.
No use of this publication may be made for resale or other
commercial purpose without the prior written permission of IUCN.
Citation: Abebe, Y. D. and Geheb, K. (Eds), 2003. Wetlands of Ethiopia.
Proceedings of a seminar on the resources and status of Ethiopia’s
wetlands , vi + 116pp.
ISBN: 2-8317-0689-0
Design and layout: Gordon O. Arara
Cover photographs: Front cover: Awassa wetland; Back cover: Fisherman in Awassa
© Alan Dixon, Research Fellow, Wetland and Natural Resources
Research Group, University of Huddersfield, Queensgate, Web site:
http://wetlands/hud.ac.uk
Available from: IUCN- EARO Publications Service Unit, P. O. Box 68200 – 00200,
Nairobi, Kenya; Telephone ++ 254 20 890605-12; Fax ++ 254 20
890615; E-mail: [email protected]
The designations of geographical entities in this book, and the presentation of the material, do not
imply the expression of any opinion whatsoever on the part of the participating organizations
concerning the legal status of any country, territory, or area, or of its authorities, or concerning the
delimitation of its frontiers or boundaries.
The opinions expressed by the authors in this publication do not necessarily represent the view of
IUCN.
The IUCN Seminar on the Wetlands of Ethiopia acknowledges the generous support of the Royal
Netherlands Embassy, Addis Ababa.
IUCN – The World Conservation Union
IUCN – The World Conservation Union was founded in 1948 and brings together 79
states, 112 government agencies, 760 NGOs, 37 affiliates, and some 10,000 scientists
and experts from 141 countries in a unique worldwide partnership. Its mission is to
influence, encourage and assist societies throughout the world to conserve the integrity
and diversity of nature and to ensure that any use of natural resources is equitable and
ecologically sustainable. Within the framework of global conventions IUCN has helped
over 75 countries to prepare and implement national conservation and biodiversity
strategies. IUCN has approximately 1000 staff, most of whom are located in its 42
regional and country offices while 100 work at its headquarters in Gland, Switzerland.
IUCN Wetlands and Water Resources Programme
The IUCN Wetlands and Water Resources Programme coordinates and reinforces
activities of the Union concerned with the management of wetland and water
ecosystems. The Programme focuses upon the conservation of ecological and
hydrological processes, in particular by developing, testing, and promoting means of
sustainable utilisation of wetlands. It does so in collaboration with IUCN members and
partners, in particular those other international institutions with a specific wetland
mandate, especially the Ramsar Convention Bureau, and the International Waterfowl
and Wetlands Research Bureau (IWRB).
The core of the Programme is a series of field projects which develop the methodologies
for wetland management, in particular in the countries of the developing world where
wetlands are used intensively by local communities which depend upon these for their
well-being. Related strategic and policy initiatives draw upon the results of these
projects and present their conclusions in a form useful for government decision makers
and planners.
The activities of the Programme are designed on the basis of the concerns and
information provided by IUCN members. To facilitate this, the Programme works
through IUCN’s regional offices. The Programme also works closely with the major
development assistance agencies to ensure that conservation considerations are
adequately addressed in their projects.
The Wetlands and Water Resources Programme receives generous financial support
from the World Wide Fund For Nature (WWF), the Swiss Directorate of Development
Cooperation and Humanitarian Aid (DDA), the Finnish International Development
Agency (FINNIDA) and the Government of the Netherlands. Project support has been
received from the Swedish International Development Authority (SIDA), Norwegian
Agency for Development Cooperation (NORAD), United States Agency for
International Development (USAID), the Ford Foundation and a number of IUCN
members including the Finnish Association for Nature Conservation (FANC), Institut
Francais pour Le Developpement en Cooperation (ORSTOM), the Royal Society for the
Protection of Birds (RSPB), the United States National Park Service (USNPS) and the
World Wide Fund For Nature (WWF). It is coordinated from the IUCN Headquarters in
Switzerland, with regional coordinators in Central America, South America, Brazil,
West, East and Southern Africa, and Asia.
Table of Contents
Wetlands of Ethiopia: an introduction……………………………………………………………….. 1
Yilma D. Abebe
The distribution and status of Ethiopian wetlands: an overview……………………………..12
Leykun Abunje
Biodiversity potentials and threats to the southern
Rift Valley lakes of Ethiopia…………………………………………………………………………..18
Lemlem Sissay
Wetlands, birds and important bird areas in Ethiopia …………………………………………..25
Mengistu Wonderfrash
Wetlands research in south-western Ethiopia: the experience of the
Ethiopian Wetlands Research Programme …………………………………………………………37
Afework Hailu
Wetland plants in Ethiopia with examples from
Illubabor, south-western Ethiopia…………………………………………………………………….49
Zerihun Woldu and Kumlachew Yeshitela
Wetlands, gender and poverty: some elements in the development
of sustainable and equitable wetland management ………………………………………………58
Adrian Wood
Challenges and opportunities of Ethiopian wetlands: the case
of Lake Awassa and its feeders………………………………………………………………………..67
Zerihun Desta
Water resources policy and river basin development as related to wetlands……………..76
Messele Fisseha
Wetlands policy development in Ethiopia………………………………………………………….81
Dessalagne Mesfin
Environmental impact assessment and the wise use of wetlands…………………………….86
Berhanu Tekaligne
Towards Sustainable Wetlands Management: The Ugandan Experience………………….97
Reint J. Bakema and Paul Mafabi
Appendix I. Ethiopian Wetlands…………………………………………………………………….108
Seminar attendance……………………………………………………………………………………..111
Contributors……………………………………………………………………………………………….113
Other titles in this series……………………………………………………………………………….114
1
Wetlands of Ethiopia: an introduction
Yilma D. Abebe
Regional Wetlands Programme
IUCN Eastern Africa Regional Office
P. O. Box 68200
Nairobi
Kenya
An introduction to wetlands
Wetlands are ecosystems or units of the landscape that are found on the interface
between land and water. While water is a major factor of wetland definition (Ramsar
Convention Bureau, 1997), soils, vegetation and animal life also contribute to their
unique characteristics (Koetze, 1996; Howard, 1995; Roggeri, 1995). As a result, it has
proved difficult to define wetlands, and over 50 definitions exist. That used by the
Ramsar Convention (1997: 2) is as follows:
“areas of marsh, fen, peatland or water, whether natural or artificial, permanent or
temporary, with water that is static or flowing, fresh, brackish or salt, including
areas of marine water the depth of which at low tide does not exceed six meters”.
This definition provides significant latitude – wetlands, as a result, come in a whole host
of forms and types. The Ramsar Convention recognises five major wetland systems
(Ramsar Convention Bureau, 1997), while others identify up to seven main groupings
(Dugan, 1990). The major Ramsar groupings are:
– marine (coastal wetlands);
– estuarine (deltas, tidal marshes, and mangroves);
– lacustrine (lakes and associated wetlands);
– riverine (rivers, streams and associated wetlands);
– palustrine (marshes, swamps and bogs).
These forms are further divided into more than 30 sub-divisions classifying them
according to physical, chemical or biological characteristics.
Wetlands are distributed all over the globe and are estimated to cover about 6% of the
earth’s surface (Maltby, 1986) – some 5.7 million km2 (WCMC, 1992). Although Africa
is best known for its savannahs and hot deserts, 1% of its surface area (345,000 km2) is
covered by wetlands (Finlayson and Moser, 1991). These ecosystems range from the
Senegal River and the Inner Niger Deltas in the West, to the Sudd Floodplains and the
Ethiopian Wetlands in the East. Southwards, important wetlands include the Zaire Basin
Swamps, the Okavango Inland Delta, the Kafue Flats, the African Great Lakes and the
extensive Malagarasi-Moyovosi Wetlands in Tanzania. Wetland characteristics will also
vary with altitude, with high ground wetlands, such as those found in the Ethiopian and
Kenyan mountain systems, complementing lowland types found in the semi-desert.
Wetlands of Ethiopia
2
Wetlands have played a noticeable role in the growth of human civilisations and cultural
development. This is true globally, where major pre-historic civilisations, including
those on the Nile, Euphrates and Tigris, have emerged and developed (Finlayson and
Moser, 1991). It is noteworthy that the Great Rift Valley of Africa has yielded fossil
evidence of some of the world’s earliest hominids. This is especially true in the
Ethiopian Rift. Fossil remains from Hadar in the Afar depression, and at Omo in
Southern Ethiopia, suggest that in order for humans to have lived here, the Ethiopian
Rift must at one time have been better watered than it is presently. The Rift’s ever
changing geology, which was marked by the slow sedimentation of rivers and changes
in drainage and faulting, created ideal conditions for the rise and later development of
the hominids (Smith, 1995).
The importance of wetlands
Only 2.6% of the world’s water is fresh (Illueca and Rast, 1996). The remainder is
found in the oceans and brackish waters. Only a fraction of the world’s fresh water is
available for consumption because so much of it is locked up in polar icecaps and
glaciers (Illueca and Rast, 1996).
Freshwater resources are a finite, but global consumption rates are known to increase 2-
3% every year (Illueca and Rast, 1996). Africa uses only 4% of its renewable freshwater
resources because of the uneven distribution of water resources over the continent
(UNEP, 2000). At the same time, access to water is affected by its quality – much of
Africa’s water may be unsuitable for consumption by its people. These regional patterns
are also evident in Ethiopia, where water resources are unevenly distributed and only a
quarter of its population has access to safe water and sanitation.
Wetlands are the main custodians of these valuable water resources. They act as ‘banks’
from where water may be drawn, and groundwater replenished. Dugan (1990) explains
that wetland values are best understood in terms of their intrinsic conditions (biological,
chemical and physical), which allow them to carry out their distinctive functions and
generate products. Their functions comprise those natural processes that sustain
economic activities and fortify ecological integrity. Examples are groundwater
discharge and recharge, flood control, shoreline stabilisation and nutrient retention.
Besides water being the most basic product that a wetland can provide, food, fuel wood,
wildlife, fisheries, forage and agricultural resources are additional wetland products.
Wetland attributes are closely intermeshed with the ethical and aesthetic values that
human beings attach to them (Roggeri, 1995).
Wetlands are the most productive ecosystems in the world, by far outstripping some of
the alternative uses to which they are subjected. The annual primary production of
herbaceous swamps, for example, is impressive. Papyrus in tropical Africa can produce
up to 143 tonnes per hectare, while production rates for Typha range from 30 to 70
tonnes per hectare. Conversely, highly productive crops such as sugar cane and maize
produce just 63 tonnes and 60 tonnes per hectare respectively (Finlayson and Moser,
1991).
Wetlands of Ethiopia: an introduction
3
Threats to wetlands
While wetlands may be the most productive of ecosystems on earth, they are also the
most threatened. Wetland destruction and alteration has been and is still seen as an
advanced mode of development, even at the government level. Wetlands and their value
remain little understood and their loss is increasingly becoming an environmental
disaster. While rates of wetland loss are documented for the developed world, the
limited study of these ecosystems in countries like Ethiopia leaves us with little to say.
Wetland loss is evident wherever major developments like dams, irrigation schemes and
conversion projects are present in the developing world. While most of the threats that
wetlands face result from their misuse, many are also related to unsustainable resource
extraction. Another important reason for their vulnerability is the fact that they are
dynamic systems undergoing continual change (Barbier et al., 1996). As a result, many
wetlands are temporary features that disappear, reappear and re-create themselves over
time (Barbier et al. 1996).
Humans usually and very dramatically accelerate natural processes often unintentionally
but usually in the course of activities like agriculture, industry and urban development.
These activities can involve anything from drainage and diverting water, to dredging
and loading water sources with toxic chemicals. Perhaps the most destructive of all
activities is mining (Williams, 1990) which permanently destroys the substrate and
prevents the natural restoration of a site. Wetlands whose biotic balance has been
disturbed can often recover.
Dugan (1990) claims that 65% of wetland disturbances are of human origin, while the
remainder have natural origins. Out of these, 73% of disturbances are thought to result
from direct human actions, while the remaining 27% are believed to come from indirect
sources (Table 1).
Table 1. Causes of Wetland loss (after Dugan, 1990)
Human Actions
Direct Indirect Natural Causes
Drainage Sediment diversion Subsidence
Dredging Hydrological alterations Sea-level rise
Filling Subsidence Drought
Conversion Hurricanes and storms
Construction Erosion
Discharge Biotic effects
Mining
Abstraction
The results of wetland loss are far-reaching and disastrous. Humans and other life close
to wetlands, and who depend upon them, are the first to feel the impact of wetland loss.
Dam construction can significantly impact the lives of people living downstream, as
Wetlands of Ethiopia
4
waters are regulated. Animal and plant life dependent on a dammed river’s annual
floods may be exterminated or become endangered. Dams affect flooding cycles, water
chemistry, sediment behaviour and fish migrations (Maltby, 1986). All too often,
wetland functions, including flood protection, nutrient retention, erosion control or
sediment retention, will be compromised by well-meant development interventions.
Once a wetland has been destroyed, the services it previously provided now have to be
paid for by tax payers (Dugan, 1990). Examples of wetland services artificially
performed by human interventions are water purification and erosion control schemes
(Dugan, 1990). While industrialised countries can probably pay for most of these
services from tax incomes, this is not so in developing countries, where wetland
destruction can have a very serious impact on the livelihoods of the rural poor.
The wise use of wetlands
At its meeting in Regina, Canada in June 1987, the Ramsar Convention defined ‘wise
use’ as follows: “the wise use of wetlands is their sustainable utilisation for the benefit
of mankind in a way compatible with the maintenance of the natural properties of the
ecosystem” (Davis, 1993). The term ‘wise use’ encapsulates the need to safeguard the
integrity of wetlands while at the same time providing sustenance to the natural and
human communities around them. This position was clarified at the first meeting of the
Ramsar contracting parties in Cagliari, Italy, when it was emphasised that the “wise use
of wetlands involves the maintenance of their ecological character as a basis not only
for nature conservation, but for sustainable development” (Davis, 1993).
It goes without saying that the wise use of wetlands is impractical if the people who
make use of them are not involved in one way or another. The involvement of such
people and a knowledge of their values is the basis for the implementation of wise use
strategies. If many of the causes of wetland degradation and loss are of socio-economic
origin, then social and economic factors need to form the crux of wise use programmes.
In particular, indigenous populations should be the beneficiaries of the improved
management of wetland sites (Davis, 1993). The wise use of wetlands is a complex
concept to implement and requires the support of national programmes addressing
several factors including information, policy, research, awareness, management and
institution building (Dugan, 1990).
Ethiopia and its wetlands
Ethiopia is a country in North-Eastern Africa lying between 8º 00’ N and 38º 00’ E. Its
area covers an estimated 1,127,000 km2 of which some 7,444 km2 is covered by water.
Ethiopia has 5,311 km of frontiers that it shares with Djibouti, Eritrea, Kenya, Somalia
and Sudan.
Ethiopia’s ecological diversity and climatic variation is to a large extent explained by its
highly variable topography. Altitudes range from 125 m below sea level in the Dallol
Depression, to 4,620 m above sea level at Ras Dashen. These altitudinal extremes mean
that Ethiopia is a country of enormous habitat diversity, which is also influenced by the
country’s climate. The tropical monsoon rainfall pattern is influenced by moisture-laden
Wetlands of Ethiopia: an introduction
5
winds from the Atlantic and the Indian Ocean and also by the Inter-tropical
Convergence Zone and variations in altitude variation.
With the exception of coastal and marine-related wetlands and extensive swamp-forest
complexes, all forms of wetlands are represented in Ethiopia. These include alpine
formations, riverine, lacustrine, palustrine and floodplain wetlands. Floodplains are
found both in Ethiopia’s highlands and lowlands, although they are most common in the
North-Western and Western Highlands, Rift Valley and Eastern Highlands. Hillman and
Abebe (1993) estimate that wetlands cover 1.14% of the total landmass of the country,
while forests cover approximately 2%. Rivers from the Ethiopian Highlands annually
produce in excess of 110 billion m3 of water, of which 74% flows into rivers draining
into Sudan, Egypt, Kenya and Somalia.
In a country like Ethiopia, a wise use wetland programme would need a responsible
agency to co-ordinate national action. Because wetlands fall within the ambit of a
crosscutting issue like environmental protection, both public and private institutions
would need to contribute their expertise and work together. The development of a
management plan for Ethiopia’s wetlands will need basic studies, including awareness,
surveys and inventories, which should be part and parcel of a wetland development
programme (Davis, 1993; Ramsar, 1997).
Some of the institutions that could take the lead in the development of a wise use
wetlands management plan for Ethiopia have already been involved in wetlands-related
work for some time. These are:
– the Ethiopian Wildlife Conservation Organisation (EWCO): wetland distribution,
preliminary mapping and gathering information, protected area management;
– Ethiopian Wildlife and Natural History Society (EWNHS): wetland birds,
identification of wetland Important Bird Areas (IBAs) and promoting the research
and management of threatened species;
– Ethiopian Wetlands Research Project (EWRP): indigenous knowledge, sustainable
management, socio-economic processes, equity/gender, and cultural values;
– Environmental Protection Authority (EPA): environmental policy, conservation
strategies and Environmental Impact Assessment (EIA) procedures;
– Institute for Biodiversity Conservation Research (IBCR): biodiversity conservation
in Ethiopian Rift Valley Lakes;
– Addis Ababa University: amongst others, limnological studies, wetland
biodiversity and social studies.
An over-view of wetlands work in Ethiopia
It was with the kind and generous support of the Royal Netherlands Embassy in Addis
Ababa that the first ever meeting on the wetlands of Ethiopia was possible. The meeting
brought together major stakeholders from the country’s wetland conservation arena to
discuss and look at wetland issues more closely than they have been considered in the
past. The meeting’s final resolution aimed to create a core team comprising various
institutions to look at wetland conservation and management. The papers presented in
this volume look at wetlands from various angles.
Wetlands of Ethiopia
6
The first paper, by Leykun Abunie, sets out to try and classify Ethiopia’s wetlands. He
starts by grouping them broadly into four biomes. At a far more localised level, Abunie
goes on to group Ethiopian wetlands by habitat, physical and biological characteristics,
yielding ten different groups. Like many of the other papers in this volume, Abunie
identifies the main threats facing wetlands as relating to their drainage and to human
activities in their catchment areas.
Lemlem Sissay’s paper concerns the value of wetlands, and considers Ethiopia’s Rift
Valley lakes. She argues that they are of extremely high value in terms of the wetland
functions that they provide, the biodiversity that they support and the economic values
that they generate. She then identifies a series of threats to these valuable resources as
high population pressure, wood harvesting and other excessive natural resource
exploitation in wetland drainage basins.
Mengistu Wondefrash’s paper builds upon the introduction to wetlands presented here.
He argues that in Ethiopia, there is a lack of awareness of the wetland ‘concept’, too few
resources to provoke wetlands conservation, a derth of tools or documents to ensure the
formulation of an adequate national wetlands policy, few focal groups – in the
government or otherwise – through which wetland issues may be channelled and,
finally, a lack of a sense of responsibility for the protection and wise use of wetlands.
Wondefrash summarises what he sees as the major threats facing wetlands as
demographic pressures, development pressures, pollution, mis-management and weed
infestation.
The vital importance of wetlands as ecological reserves is also considered in
Wondefrash’s paper when he summarises the role that they play in the conservation of
bird life. Hence, many wetlands conservation initiatives will concentrate their efforts on
the preservation of birds, not least as valuable indicators of biodiversity and ecosystem
health. He points out that migratory waterfowl often use a multitude of wetlands as they
travel to and from their migratory destinations, necessitating that wetland conservation
approaches need to be international in scope and organisation. Wondefrash then goes on
to discuss Ethiopia’s Important Bird Areas (IBAs) and demonstrates the critical
importance of these habitats in the protection and conservation of many of Ethiopia’s
most threatened bird species.
Wondefrash concludes with a series of management recommendations that include the
raising of public awareness, the need for national advocacy roles, a conservation action
plan, research and monitoring at selected wetlands and the need to develop a focal
institution for wetlands. Amongst these, he calls for participatory approaches in the
management and monitoring of wetlands, pointing out how necessary this is in the light
of Ethiopia’s enormous and growing human population.
Afework Hailu’s paper is the first of three to discuss the output of the Ethiopian
Wetlands Research Programme (EWRP). The study was based in Illubabor in southwest
Ethiopia, and concentrated on eight ‘core’ wetlands. A multi-disciplinary approach was
employed to not only consider the physical parameters of these swamps, but also to
examine the characteristics and use values of the swamps to surrounding human
populations. As can be expected, the physical work on these swamps was to determine
that substantial changes occur when they are drained or heavily exploited. Importantly,
Hailu claims that amongst the surrounding populations there is evidence of traditional
Citations (2)
References (95)
Article
- Oct 2018
ViewShow abstract
Article
- Nov 2007
- LAND DEGRAD DEV
ViewShow abstract
Recommendations
Project
Mercury Dynamics in the Food Webs of the Ethiopian Rift Valley Lakes.
Article
Land use change and its drivers in Kurt Bahir wetland, north-western Ethiopia
May 2017 · African Journal of Aquatic Science
The effects of land-use change on ecosystem services in Kurt Bahir wetland were investigated during 2013 to 2014 using LANDSAT satellite images from 1973, 1986, 2002 and 2013 to identify and map changes in land-use classes over time. To understand perceptions of changes in ecosystem services that resulted from observed land-use changes discussions were held with local key informants and focus … [Show full abstract]
Article
Development of a multimetric plant-based index of biotic integrity forassessing the ecological state…
July 2016 · Ecological Indicators
Article
Indigenous Management of Wetlands: Experiences in Ethiopia. By A. B. Dixon. Aldershot: Ashgate (2003…
April 2004 · Experimental Agriculture
Article
Full-text available
Shesher and Welala Floodplain Wetlands (Lake Tana, Ethiopia): Are They Important Breeding Habitats f…
April 2012 · The Scientific World Journal
This study aims at investigating the spawning migration of the endemic Labeobarbus species and C. gariepinus from Lake Tana, through Ribb River, to Welala and Shesher wetlands. The study was conducted during peak spawning months (July to October, 2010). Fish were collected through overnight gillnet settings. A total of 1725 specimens of the genus Labeobarbus (13 species) and 506 specimens of C. … [Show full abstract]
Article
Full-text available
The food and feeding habits of the African catfish, Clarias gariepinus (Burchell, 1822) (Pisces: Cla…
March 2016
Company
Support
Business solutions
© 2008-2022 ResearchGate GmbH. All rights reserved.
ChapterPDF Available
Wetlands of Ethiopia
- January 2003
- In book: Wetlands of Ethiopia (pp.67-75)
- Edition: 1st
- Chapter: 8
- Publisher: IUCN – The World Conservation Union
- Editors: Yilma D. Abebe and Kim Geheb
Authors:
Citations (2)References (95)Figures (4)
Figures
Map of Ethiopia showing the regions and positions of neighbouring countries
Broad strategies used in the National Wetlands Programme to improve wetland management in Uganda
. Details of the core wetland sites where biodiversity monitoring was undertaken
No caption available
…
Figures – uploaded by Zerihun Desta Beshah
Author content
Content may be subject to copyright.
Discover the world’s research
- 20+ million members
- 135+ million publications
- 700k+ research projects
Public Full-text 1
Content uploaded by Zerihun Desta Beshah
Author content
Content may be subject to copyright.
Wetlands of Ethiopia
Proceedings of a seminar on the resources and
status of in Ethiopia’s wetlands
Yilma D. Abebe and Kim Geheb(Editors)
IUCN – The World Conservation Union
Founded in 1948, The World Conservation Union brings together States,
government agencies and a diverse range of non-governmental organisations
in a unique world partnership: over 980 members in all, spread across some
140 countries.
As a Union, IUCN seeks to influence, encourage and assist societies
throughout the world to conserve the integrity and diversity of nature and to
ensure that any use of natural resources is equitable and ecologically
sustainable.
The World Conservation Union builds on the strengths of its members,
networks and partners to enhance their capacity and to support global
alliances to safeguard natural resources at local, regional and global levels.
IUCN Wetlands and WaterResources
Programme
Rue Mauverney 28
CH-1196 Gland, Switzerland
Tel: + 41 22 999 0001
Fax: + 41 22 999 0002
E-mail:[email protected]
www.iucn.org/themes/wetlands/
IUCN Eastern Africa
Regional Office
P. O. Box 68200-00200
Nairobi, Kenya
Tel: ++ 254 20 890605-12
Fax: ++ 254 20 890615/407
E-mail: [email protected]
IUCN
Wetlands
and Water
Resources
Programme
IUCN
Wetlands of Ethiopia
BLUE SERIES
Wetlands of Ethiopia
Proceedings of a seminar on the resources and
status of Ethiopia’s wetlands
Editors
Yilma D. Abebe and Kim Geheb
IUCN
2003
Published by: IUCN
Copyright: 2003. International Union for Conservation of Nature and Natural
Resources
This publication may be produced in whole or part and in any form
for education or non-profit uses, without special permission from the
copyright holder, provided acknowledgement of the source is made.
IUCN would appreciate receiving a copy of any publication which
uses this publication as a source.
No use of this publication may be made for resale or other
commercial purpose without the prior written permission of IUCN.
Citation: Abebe, Y. D. and Geheb, K. (Eds), 2003. Wetlands of Ethiopia.
Proceedings of a seminar on the resources and status of Ethiopia’s
wetlands , vi + 116pp.
ISBN: 2-8317-0689-0
Design and layout: Gordon O. Arara
Cover photographs: Front cover: Awassa wetland; Back cover: Fisherman in Awassa
© Alan Dixon, Research Fellow, Wetland and Natural Resources
Research Group, University of Huddersfield, Queensgate, Web site:
http://wetlands/hud.ac.uk
Available from: IUCN- EARO Publications Service Unit, P. O. Box 68200 – 00200,
Nairobi, Kenya; Telephone ++ 254 20 890605-12; Fax ++ 254 20
890615; E-mail: [email protected]
The designations of geographical entities in this book, and the presentation of the material, do not
imply the expression of any opinion whatsoever on the part of the participating organizations
concerning the legal status of any country, territory, or area, or of its authorities, or concerning the
delimitation of its frontiers or boundaries.
The opinions expressed by the authors in this publication do not necessarily represent the view of
IUCN.
The IUCN Seminar on the Wetlands of Ethiopia acknowledges the generous support of the Royal
Netherlands Embassy, Addis Ababa.
IUCN – The World Conservation Union
IUCN – The World Conservation Union was founded in 1948 and brings together 79
states, 112 government agencies, 760 NGOs, 37 affiliates, and some 10,000 scientists
and experts from 141 countries in a unique worldwide partnership. Its mission is to
influence, encourage and assist societies throughout the world to conserve the integrity
and diversity of nature and to ensure that any use of natural resources is equitable and
ecologically sustainable. Within the framework of global conventions IUCN has helped
over 75 countries to prepare and implement national conservation and biodiversity
strategies. IUCN has approximately 1000 staff, most of whom are located in its 42
regional and country offices while 100 work at its headquarters in Gland, Switzerland.
IUCN Wetlands and Water Resources Programme
The IUCN Wetlands and Water Resources Programme coordinates and reinforces
activities of the Union concerned with the management of wetland and water
ecosystems. The Programme focuses upon the conservation of ecological and
hydrological processes, in particular by developing, testing, and promoting means of
sustainable utilisation of wetlands. It does so in collaboration with IUCN members and
partners, in particular those other international institutions with a specific wetland
mandate, especially the Ramsar Convention Bureau, and the International Waterfowl
and Wetlands Research Bureau (IWRB).
The core of the Programme is a series of field projects which develop the methodologies
for wetland management, in particular in the countries of the developing world where
wetlands are used intensively by local communities which depend upon these for their
well-being. Related strategic and policy initiatives draw upon the results of these
projects and present their conclusions in a form useful for government decision makers
and planners.
The activities of the Programme are designed on the basis of the concerns and
information provided by IUCN members. To facilitate this, the Programme works
through IUCN’s regional offices. The Programme also works closely with the major
development assistance agencies to ensure that conservation considerations are
adequately addressed in their projects.
The Wetlands and Water Resources Programme receives generous financial support
from the World Wide Fund For Nature (WWF), the Swiss Directorate of Development
Cooperation and Humanitarian Aid (DDA), the Finnish International Development
Agency (FINNIDA) and the Government of the Netherlands. Project support has been
received from the Swedish International Development Authority (SIDA), Norwegian
Agency for Development Cooperation (NORAD), United States Agency for
International Development (USAID), the Ford Foundation and a number of IUCN
members including the Finnish Association for Nature Conservation (FANC), Institut
Francais pour Le Developpement en Cooperation (ORSTOM), the Royal Society for the
Protection of Birds (RSPB), the United States National Park Service (USNPS) and the
World Wide Fund For Nature (WWF). It is coordinated from the IUCN Headquarters in
Switzerland, with regional coordinators in Central America, South America, Brazil,
West, East and Southern Africa, and Asia.
Table of Contents
Wetlands of Ethiopia: an introduction……………………………………………………………….. 1
Yilma D. Abebe
The distribution and status of Ethiopian wetlands: an overview……………………………..12
Leykun Abunje
Biodiversity potentials and threats to the southern
Rift Valley lakes of Ethiopia…………………………………………………………………………..18
Lemlem Sissay
Wetlands, birds and important bird areas in Ethiopia …………………………………………..25
Mengistu Wonderfrash
Wetlands research in south-western Ethiopia: the experience of the
Ethiopian Wetlands Research Programme …………………………………………………………37
Afework Hailu
Wetland plants in Ethiopia with examples from
Illubabor, south-western Ethiopia…………………………………………………………………….49
Zerihun Woldu and Kumlachew Yeshitela
Wetlands, gender and poverty: some elements in the development
of sustainable and equitable wetland management ………………………………………………58
Adrian Wood
Challenges and opportunities of Ethiopian wetlands: the case
of Lake Awassa and its feeders………………………………………………………………………..67
Zerihun Desta
Water resources policy and river basin development as related to wetlands……………..76
Messele Fisseha
Wetlands policy development in Ethiopia………………………………………………………….81
Dessalagne Mesfin
Environmental impact assessment and the wise use of wetlands…………………………….86
Berhanu Tekaligne
Towards Sustainable Wetlands Management: The Ugandan Experience………………….97
Reint J. Bakema and Paul Mafabi
Appendix I. Ethiopian Wetlands…………………………………………………………………….108
Seminar attendance……………………………………………………………………………………..111
Contributors……………………………………………………………………………………………….113
Other titles in this series……………………………………………………………………………….114
1
Wetlands of Ethiopia: an introduction
Yilma D. Abebe
Regional Wetlands Programme
IUCN Eastern Africa Regional Office
P. O. Box 68200
Nairobi
Kenya
An introduction to wetlands
Wetlands are ecosystems or units of the landscape that are found on the interface
between land and water. While water is a major factor of wetland definition (Ramsar
Convention Bureau, 1997), soils, vegetation and animal life also contribute to their
unique characteristics (Koetze, 1996; Howard, 1995; Roggeri, 1995). As a result, it has
proved difficult to define wetlands, and over 50 definitions exist. That used by the
Ramsar Convention (1997: 2) is as follows:
“areas of marsh, fen, peatland or water, whether natural or artificial, permanent or
temporary, with water that is static or flowing, fresh, brackish or salt, including
areas of marine water the depth of which at low tide does not exceed six meters”.
This definition provides significant latitude – wetlands, as a result, come in a whole host
of forms and types. The Ramsar Convention recognises five major wetland systems
(Ramsar Convention Bureau, 1997), while others identify up to seven main groupings
(Dugan, 1990). The major Ramsar groupings are:
– marine (coastal wetlands);
– estuarine (deltas, tidal marshes, and mangroves);
– lacustrine (lakes and associated wetlands);
– riverine (rivers, streams and associated wetlands);
– palustrine (marshes, swamps and bogs).
These forms are further divided into more than 30 sub-divisions classifying them
according to physical, chemical or biological characteristics.
Wetlands are distributed all over the globe and are estimated to cover about 6% of the
earth’s surface (Maltby, 1986) – some 5.7 million km2 (WCMC, 1992). Although Africa
is best known for its savannahs and hot deserts, 1% of its surface area (345,000 km2) is
covered by wetlands (Finlayson and Moser, 1991). These ecosystems range from the
Senegal River and the Inner Niger Deltas in the West, to the Sudd Floodplains and the
Ethiopian Wetlands in the East. Southwards, important wetlands include the Zaire Basin
Swamps, the Okavango Inland Delta, the Kafue Flats, the African Great Lakes and the
extensive Malagarasi-Moyovosi Wetlands in Tanzania. Wetland characteristics will also
vary with altitude, with high ground wetlands, such as those found in the Ethiopian and
Kenyan mountain systems, complementing lowland types found in the semi-desert.
Wetlands of Ethiopia
2
Wetlands have played a noticeable role in the growth of human civilisations and cultural
development. This is true globally, where major pre-historic civilisations, including
those on the Nile, Euphrates and Tigris, have emerged and developed (Finlayson and
Moser, 1991). It is noteworthy that the Great Rift Valley of Africa has yielded fossil
evidence of some of the world’s earliest hominids. This is especially true in the
Ethiopian Rift. Fossil remains from Hadar in the Afar depression, and at Omo in
Southern Ethiopia, suggest that in order for humans to have lived here, the Ethiopian
Rift must at one time have been better watered than it is presently. The Rift’s ever
changing geology, which was marked by the slow sedimentation of rivers and changes
in drainage and faulting, created ideal conditions for the rise and later development of
the hominids (Smith, 1995).
The importance of wetlands
Only 2.6% of the world’s water is fresh (Illueca and Rast, 1996). The remainder is
found in the oceans and brackish waters. Only a fraction of the world’s fresh water is
available for consumption because so much of it is locked up in polar icecaps and
glaciers (Illueca and Rast, 1996).
Freshwater resources are a finite, but global consumption rates are known to increase 2-
3% every year (Illueca and Rast, 1996). Africa uses only 4% of its renewable freshwater
resources because of the uneven distribution of water resources over the continent
(UNEP, 2000). At the same time, access to water is affected by its quality – much of
Africa’s water may be unsuitable for consumption by its people. These regional patterns
are also evident in Ethiopia, where water resources are unevenly distributed and only a
quarter of its population has access to safe water and sanitation.
Wetlands are the main custodians of these valuable water resources. They act as ‘banks’
from where water may be drawn, and groundwater replenished. Dugan (1990) explains
that wetland values are best understood in terms of their intrinsic conditions (biological,
chemical and physical), which allow them to carry out their distinctive functions and
generate products. Their functions comprise those natural processes that sustain
economic activities and fortify ecological integrity. Examples are groundwater
discharge and recharge, flood control, shoreline stabilisation and nutrient retention.
Besides water being the most basic product that a wetland can provide, food, fuel wood,
wildlife, fisheries, forage and agricultural resources are additional wetland products.
Wetland attributes are closely intermeshed with the ethical and aesthetic values that
human beings attach to them (Roggeri, 1995).
Wetlands are the most productive ecosystems in the world, by far outstripping some of
the alternative uses to which they are subjected. The annual primary production of
herbaceous swamps, for example, is impressive. Papyrus in tropical Africa can produce
up to 143 tonnes per hectare, while production rates for Typha range from 30 to 70
tonnes per hectare. Conversely, highly productive crops such as sugar cane and maize
produce just 63 tonnes and 60 tonnes per hectare respectively (Finlayson and Moser,
1991).
Wetlands of Ethiopia: an introduction
3
Threats to wetlands
While wetlands may be the most productive of ecosystems on earth, they are also the
most threatened. Wetland destruction and alteration has been and is still seen as an
advanced mode of development, even at the government level. Wetlands and their value
remain little understood and their loss is increasingly becoming an environmental
disaster. While rates of wetland loss are documented for the developed world, the
limited study of these ecosystems in countries like Ethiopia leaves us with little to say.
Wetland loss is evident wherever major developments like dams, irrigation schemes and
conversion projects are present in the developing world. While most of the threats that
wetlands face result from their misuse, many are also related to unsustainable resource
extraction. Another important reason for their vulnerability is the fact that they are
dynamic systems undergoing continual change (Barbier et al., 1996). As a result, many
wetlands are temporary features that disappear, reappear and re-create themselves over
time (Barbier et al. 1996).
Humans usually and very dramatically accelerate natural processes often unintentionally
but usually in the course of activities like agriculture, industry and urban development.
These activities can involve anything from drainage and diverting water, to dredging
and loading water sources with toxic chemicals. Perhaps the most destructive of all
activities is mining (Williams, 1990) which permanently destroys the substrate and
prevents the natural restoration of a site. Wetlands whose biotic balance has been
disturbed can often recover.
Dugan (1990) claims that 65% of wetland disturbances are of human origin, while the
remainder have natural origins. Out of these, 73% of disturbances are thought to result
from direct human actions, while the remaining 27% are believed to come from indirect
sources (Table 1).
Table 1. Causes of Wetland loss (after Dugan, 1990)
Human Actions
Direct Indirect Natural Causes
Drainage Sediment diversion Subsidence
Dredging Hydrological alterations Sea-level rise
Filling Subsidence Drought
Conversion Hurricanes and storms
Construction Erosion
Discharge Biotic effects
Mining
Abstraction
The results of wetland loss are far-reaching and disastrous. Humans and other life close
to wetlands, and who depend upon them, are the first to feel the impact of wetland loss.
Dam construction can significantly impact the lives of people living downstream, as
Wetlands of Ethiopia
4
waters are regulated. Animal and plant life dependent on a dammed river’s annual
floods may be exterminated or become endangered. Dams affect flooding cycles, water
chemistry, sediment behaviour and fish migrations (Maltby, 1986). All too often,
wetland functions, including flood protection, nutrient retention, erosion control or
sediment retention, will be compromised by well-meant development interventions.
Once a wetland has been destroyed, the services it previously provided now have to be
paid for by tax payers (Dugan, 1990). Examples of wetland services artificially
performed by human interventions are water purification and erosion control schemes
(Dugan, 1990). While industrialised countries can probably pay for most of these
services from tax incomes, this is not so in developing countries, where wetland
destruction can have a very serious impact on the livelihoods of the rural poor.
The wise use of wetlands
At its meeting in Regina, Canada in June 1987, the Ramsar Convention defined ‘wise
use’ as follows: “the wise use of wetlands is their sustainable utilisation for the benefit
of mankind in a way compatible with the maintenance of the natural properties of the
ecosystem” (Davis, 1993). The term ‘wise use’ encapsulates the need to safeguard the
integrity of wetlands while at the same time providing sustenance to the natural and
human communities around them. This position was clarified at the first meeting of the
Ramsar contracting parties in Cagliari, Italy, when it was emphasised that the “wise use
of wetlands involves the maintenance of their ecological character as a basis not only
for nature conservation, but for sustainable development” (Davis, 1993).
It goes without saying that the wise use of wetlands is impractical if the people who
make use of them are not involved in one way or another. The involvement of such
people and a knowledge of their values is the basis for the implementation of wise use
strategies. If many of the causes of wetland degradation and loss are of socio-economic
origin, then social and economic factors need to form the crux of wise use programmes.
In particular, indigenous populations should be the beneficiaries of the improved
management of wetland sites (Davis, 1993). The wise use of wetlands is a complex
concept to implement and requires the support of national programmes addressing
several factors including information, policy, research, awareness, management and
institution building (Dugan, 1990).
Ethiopia and its wetlands
Ethiopia is a country in North-Eastern Africa lying between 8º 00’ N and 38º 00’ E. Its
area covers an estimated 1,127,000 km2 of which some 7,444 km2 is covered by water.
Ethiopia has 5,311 km of frontiers that it shares with Djibouti, Eritrea, Kenya, Somalia
and Sudan.
Ethiopia’s ecological diversity and climatic variation is to a large extent explained by its
highly variable topography. Altitudes range from 125 m below sea level in the Dallol
Depression, to 4,620 m above sea level at Ras Dashen. These altitudinal extremes mean
that Ethiopia is a country of enormous habitat diversity, which is also influenced by the
country’s climate. The tropical monsoon rainfall pattern is influenced by moisture-laden
Wetlands of Ethiopia: an introduction
5
winds from the Atlantic and the Indian Ocean and also by the Inter-tropical
Convergence Zone and variations in altitude variation.
With the exception of coastal and marine-related wetlands and extensive swamp-forest
complexes, all forms of wetlands are represented in Ethiopia. These include alpine
formations, riverine, lacustrine, palustrine and floodplain wetlands. Floodplains are
found both in Ethiopia’s highlands and lowlands, although they are most common in the
North-Western and Western Highlands, Rift Valley and Eastern Highlands. Hillman and
Abebe (1993) estimate that wetlands cover 1.14% of the total landmass of the country,
while forests cover approximately 2%. Rivers from the Ethiopian Highlands annually
produce in excess of 110 billion m3 of water, of which 74% flows into rivers draining
into Sudan, Egypt, Kenya and Somalia.
In a country like Ethiopia, a wise use wetland programme would need a responsible
agency to co-ordinate national action. Because wetlands fall within the ambit of a
crosscutting issue like environmental protection, both public and private institutions
would need to contribute their expertise and work together. The development of a
management plan for Ethiopia’s wetlands will need basic studies, including awareness,
surveys and inventories, which should be part and parcel of a wetland development
programme (Davis, 1993; Ramsar, 1997).
Some of the institutions that could take the lead in the development of a wise use
wetlands management plan for Ethiopia have already been involved in wetlands-related
work for some time. These are:
– the Ethiopian Wildlife Conservation Organisation (EWCO): wetland distribution,
preliminary mapping and gathering information, protected area management;
– Ethiopian Wildlife and Natural History Society (EWNHS): wetland birds,
identification of wetland Important Bird Areas (IBAs) and promoting the research
and management of threatened species;
– Ethiopian Wetlands Research Project (EWRP): indigenous knowledge, sustainable
management, socio-economic processes, equity/gender, and cultural values;
– Environmental Protection Authority (EPA): environmental policy, conservation
strategies and Environmental Impact Assessment (EIA) procedures;
– Institute for Biodiversity Conservation Research (IBCR): biodiversity conservation
in Ethiopian Rift Valley Lakes;
– Addis Ababa University: amongst others, limnological studies, wetland
biodiversity and social studies.
An over-view of wetlands work in Ethiopia
It was with the kind and generous support of the Royal Netherlands Embassy in Addis
Ababa that the first ever meeting on the wetlands of Ethiopia was possible. The meeting
brought together major stakeholders from the country’s wetland conservation arena to
discuss and look at wetland issues more closely than they have been considered in the
past. The meeting’s final resolution aimed to create a core team comprising various
institutions to look at wetland conservation and management. The papers presented in
this volume look at wetlands from various angles.
Wetlands of Ethiopia
6
The first paper, by Leykun Abunie, sets out to try and classify Ethiopia’s wetlands. He
starts by grouping them broadly into four biomes. At a far more localised level, Abunie
goes on to group Ethiopian wetlands by habitat, physical and biological characteristics,
yielding ten different groups. Like many of the other papers in this volume, Abunie
identifies the main threats facing wetlands as relating to their drainage and to human
activities in their catchment areas.
Lemlem Sissay’s paper concerns the value of wetlands, and considers Ethiopia’s Rift
Valley lakes. She argues that they are of extremely high value in terms of the wetland
functions that they provide, the biodiversity that they support and the economic values
that they generate. She then identifies a series of threats to these valuable resources as
high population pressure, wood harvesting and other excessive natural resource
exploitation in wetland drainage basins.
Mengistu Wondefrash’s paper builds upon the introduction to wetlands presented here.
He argues that in Ethiopia, there is a lack of awareness of the wetland ‘concept’, too few
resources to provoke wetlands conservation, a derth of tools or documents to ensure the
formulation of an adequate national wetlands policy, few focal groups – in the
government or otherwise – through which wetland issues may be channelled and,
finally, a lack of a sense of responsibility for the protection and wise use of wetlands.
Wondefrash summarises what he sees as the major threats facing wetlands as
demographic pressures, development pressures, pollution, mis-management and weed
infestation.
The vital importance of wetlands as ecological reserves is also considered in
Wondefrash’s paper when he summarises the role that they play in the conservation of
bird life. Hence, many wetlands conservation initiatives will concentrate their efforts on
the preservation of birds, not least as valuable indicators of biodiversity and ecosystem
health. He points out that migratory waterfowl often use a multitude of wetlands as they
travel to and from their migratory destinations, necessitating that wetland conservation
approaches need to be international in scope and organisation. Wondefrash then goes on
to discuss Ethiopia’s Important Bird Areas (IBAs) and demonstrates the critical
importance of these habitats in the protection and conservation of many of Ethiopia’s
most threatened bird species.
Wondefrash concludes with a series of management recommendations that include the
raising of public awareness, the need for national advocacy roles, a conservation action
plan, research and monitoring at selected wetlands and the need to develop a focal
institution for wetlands. Amongst these, he calls for participatory approaches in the
management and monitoring of wetlands, pointing out how necessary this is in the light
of Ethiopia’s enormous and growing human population.
Afework Hailu’s paper is the first of three to discuss the output of the Ethiopian
Wetlands Research Programme (EWRP). The study was based in Illubabor in southwest
Ethiopia, and concentrated on eight ‘core’ wetlands. A multi-disciplinary approach was
employed to not only consider the physical parameters of these swamps, but also to
examine the characteristics and use values of the swamps to surrounding human
populations. As can be expected, the physical work on these swamps was to determine
that substantial changes occur when they are drained or heavily exploited. Importantly,
Hailu claims that amongst the surrounding populations there is evidence of traditional
Citations (2)
References (95)
Article
- Oct 2018
ViewShow abstract
Article
- Nov 2007
- LAND DEGRAD DEV
ViewShow abstract
Recommendations
Project
Mercury Dynamics in the Food Webs of the Ethiopian Rift Valley Lakes.
Article
Land use change and its drivers in Kurt Bahir wetland, north-western Ethiopia
May 2017 · African Journal of Aquatic Science
The effects of land-use change on ecosystem services in Kurt Bahir wetland were investigated during 2013 to 2014 using LANDSAT satellite images from 1973, 1986, 2002 and 2013 to identify and map changes in land-use classes over time. To understand perceptions of changes in ecosystem services that resulted from observed land-use changes discussions were held with local key informants and focus … [Show full abstract]
Article
Development of a multimetric plant-based index of biotic integrity forassessing the ecological state…
July 2016 · Ecological Indicators
Article