Animal power, a cheap alternative for the construction of reservoirs in Ethiopia?

Similar documents
Using Cattle for Draft Power and Transport

Ethiopia. July Eritrea. Sudan. Djbouti. Somalia. Kenya ETHIOPIA. at a glance. summary. Tigray. Region. Amhara. Region. Somali. Oromiya.

Community-based irrigation management in Ethiopia: Strategies to enhance human health, livestock and crop production, and natural resource management

Gender issues in donkey use in rural Ethiopia

Ethiopia PSNP Team. South-South Learning Forum June 2010

Livestock and livelihoods spotlight ETHIOPIA

T. Hagos 1, T. Tesfay 2, S. Wayu 2, T. Atsbha 2, T. Yikaalo 2, T. Zeberh 2, T. Teshale 2, M. Ebrahim 3 and J. Wamatu 4 ICARDA)

FOOD AND AGRICULTURE ORGANIZATION

A guiding manual for the utilization of cultivated oatvetch and tree Lucerne fodder in the Africa RISING sites of the Ethiopian highlands

1.1 Role of agriculture in the Ethiopian economy

Household Water Harvesting and Small Scale Irrigation Schemes in Amhara Region

Low-cost Animal drawn implements for Vertisol management and strategies for land use intensification 1

Conservation tillage in cotton and maize fields in Malawi

COUNTRY INVESTMENT BRIEF

ETHIOPIA MONTHLY MARKET WATCH

SPATE IRRIGATION IN MALAWI: STATUS, POTENTIAL AND CHALLENGES.

The livestock sector is socially and politically. Identifying Strategies for Increasing Livestock Water Productivity in the Blue Nile Basin

Water Harvesting Technologies a Challenge to Ethiopia: in Environmental/Ecological, Health Condition and its Economic Sustainability

Use of Cows for Draft Work

FACTSHEET INTRODUCTION. help rebalance the water cycle, mitigate the effects of climate change and improve human health and livelihoods.

Drought Conditions and Management Strategies in Botswana

Report from an early win project

CLIMATE CHANGE ADAPTATION PROGRAMME IN WATER AND AGRICULTURE IN ANSEBA REGION, ERITREA

FROM PLOT TO WATERSHED MANAGEMENT: EXPERIENCE IN FARMER PARTICIPATORY VERTISOLS TECHNOLOGY GENERATION AND ADOPTION IN HIGHLAND ETHIOPIA 1

DAIRY TECHNOLOGY IMPACTS ON LIVEHOODS OF DAIRY PRODUCERS IN CENTRAL ETHIOPIA

Livelihood Profile Amhara Region, Ethiopia

The Northeastern region of Brazil, which is also home to the Amazon Basin, is the area that is least suitable

Climate change adaptation strategies in mixed crop-livestock systems

Challenges of commodity value chain development towards improving the competitiveness of agricultural commodity in Africa

Cereal Marketing and Household Market Participation in Ethiopia: The Case of Teff, Wheat and Rice

An Overview of Agricultural Mechanization in Sub Saharan Africa

Food Insecurity and Its Socioeconomic Consequences: The Case of Shashemene Woreda, Oromiya National Regional State, Ethiopia

Livelihood Profile Oromiya Region, Ethiopia

Traditional Beef Cattle Fattening and constraints in Damot Pullassa Woreda, Wolaita Zone, Sothern Ethiopia

International Journal of Mathematical Archive-3(4), 2012, Page: Available online through ISSN

Integrated Rainwater Harvesting Practices and Household Livelihood:

D. Abate 1, B. Tassew 1, A. Zeleke 1, A. Kedu 1 and J. Wamatu 2. International Center for Research in Dry Areas

13. Integrated Water Resource Management for Increasing Productivity and Water Use Efficiency in the Rain-fed Areas of India

Status and trends of major non timber forest products trade in Ethiopia

Assessment of Beef Cattle Fattening and Marketing System in East Badawacho District, Hadiya Zone, SNNPRS, Ethiopia

McGill Conference on Global Food Security September 25 26, 2008

TECA. Zero-grazing of improved cattle breeds using drought tolerant fodder in Uganda. TECHNOLOGIES and PRACTICES for SMALL AGRICULTURAL PRODUCERS

D. Abate 1, B. Tasswe 1, A. Zeleke 1, A. Kedu 1 and J. Wamatu 2. International Center for Research in Dry Areas

Wealth ranking in a caste area of India

REGIONAL TRAINING MODUAL MONITORING & EVALUATION OF MICRO IRIGATION PROJECTS

Flood Based Farming Practices in Tigray: Status and Potential

RAIN Foundation and its Partners in Ethiopia and MUS Integration August 2009

Climate Change and Agriculture Adaptation and Mitigation

Experiences of VSF-Suisse towards the development of Fodder Production in Mandera County Prepared by Dr. Diana Onyango Program Manager VSF-Suisse

Fighting famine and poverty through water harvesting in Northern Ethiopia

Fodder Security and Climate Change

WHY GROW MEDIC? Training Kit No. 1

Improving Water Productivity of Crop- Livestock Systems in Drought-prone Regions

Training on Roads for Water and Resilience

to the House Appropriations Subcommittee on Agriculture, Rural Development, Food and Drug Administration, and Related Agencies

ZIMBABWE CASE STUDY ZIMBABWE: COPING WITH DROUGHT AND CLIMATE CHANGE DECEMBER Country. Region. Key Result Area. UNDP Project ID 3785

Basline Servey of Irrigation and Rainfed Agriculture in Blue Nile Basin

Improving the water productivity of livestock: An opportunity for poverty reduction

ANH Academy Week, Addis Ababa, Ethiopia, June 2016

Policies for livestock development in the Ethiopian highlands

The Role of Irrigation in Agricultural Development and Poverty Alleviation at Rural Community of Iran

El Niño in Ethiopia Early impacts of drought in South Tigray Zone

How to Promote Sustainable Agriculture in Africa? Stein Holden Professor Norwegian University of Life Sciences

Zero Tillage or Reduced Tillage: The Key to Intensification of the Crop Livestock System in Ethiopia

Ethiopia. April Eritrea. Sudan. Djbouti. Somalia. Kenya ETHIOPIA. at a glance. summary. Tigray. Region. Amhara. Region. Somali. Oromiya.

THE INTER-SESSIONAL PANEL OF THE UNITED NATIONS COMMISSION ON SCIENCE AND TECHNOLOGY FOR DEVELOPMENT December 2010 Geneva UGANDA CONTRIBUTION

Addressing gender inequalities in Ethiopia s agricultural sector to reduce poverty

CHARACTERIZATION OF THE EXISTING SOIL MANAGEMENT IN RELATION TO SOME SELECTED PHYSICO-CHEMICAL PROPERTIES AT BULEHORAWOREDA, WEST GUJI ZONE

SNNPR Livelihood Profile

Rashid Ali Khan, FAO (Ret.) Gurgaon, Haryana

Unit 7 Expansion of Europe

Stakeholder Consultation Workshop Report: Ethiopia, Ghana and Tanzania Identifying and prioritizing constraints and opportunities

Ethiopian Agricultural Transformation Agency, Addis Ababa, Ethiopia; 2

Ethiopia. Grain and Feed Annual. Annual Report

Food & Nutrition Security

Case Study. Irrigated and integrated agro production systems help Mozambique adapt to climate change. SDGs addressed CHAPTERS.

The rapid rise of agricultural mechanization in Myanmar

International Journal of Modern Pharmaceutical Research IJMPR

ETHIOPIA Food Security Update July 2006

Conserving strength Canadian-backed projects assist Ethiopian communities in restoring agricultural stability

Le rôle du Groupe de la Banque africaine de développement dans le financement de l agriculture irriguée: Exemples de la Gambie et du Ghana

Summary Report. Federal Democratic Republic of Ethiopia

Seasonal Climate Variability dependent effects of Conservation Agriculture practices across different Agroecologies in Ethiopia

Multiple uses of rural household water supplies for livelihood in Ethiopia

WEATHER RISK INSURANCE FOR SMALL FARMERS IN MALAWI

Cost and Benefit of Catchment Management and Regreening in Tigray, Ethiopia

IPMS ATLAS 2007 ADAA WOREDA, OROMIYA. Table of contents. Ada a Woreda geography. Ada a peasant associations. Agroclimatic zones

Over the last three to four decades, farmers in. Economic Benefits of Rainwater Harvesting Technologies to Farmers:

SynergybetweenTraditionalandIntroducedSustainableLandManagementPracticesinEthiopia

Water-Irrigation for Food Security in Amhara National Regional State

MONITORING PRODUCTIVITY OF WATER IN AGRICULTURE AND INTERACTING SYSTEMS: THE CASE OF TEKEZE/ATBARA RIVER BASIN IN ETHIOPIA

Low input aquaculture systems in Lao PDR

Impact of Water Scarcity on Pastoral Systems: Experience from the Drought and the El Niño Rains in the Greater Horn of Africa

Challenges of Maintaining the Terraces in the Highlands

Livelihood Profile Tigray Region, Ethiopia

Planning for Success and Lessons Learned

NORDIC CLIMATE FACILITY (NCF) Promoting Renewable Energy Technologies for Enhanced Rural Livelihoods

Production of Upland Rice and Constraints Faced by the Farmers in Tselemti District, Northern Ethiopia

Food Security Situation in Ethiopia : The Case of Amhara National Regional State 0

Lesson Plan. Activity # 1. Adapting to Climate Change in the East African Savanna Objectives. Time: Summary: Materials: Background.

Transcription:

1 Animal power, a cheap alternative for the construction of reservoirs in Ethiopia? Abiye Astatke, Kai Sonder, Girma Tadesse and Don Peden Abstract Water for crop production as well as human and animal consumption is a limiting factor in most areas of Ethiopia. Due to restricted accessibility humans as well as animals spend a great amount of time and energy to reach and gather water. At the same time, Ethiopia has the greatest livestock population in Africa and about 14 million oxen available. These oxen are used almost exclusively for seasonal land preparation in cropping systems and remain unproductive during the remainder of the year. During the socialist regime in Ethiopia, community based work with draught oxen was used in two Peasant Associations to construct two ponds of 9,500 and 8,700 m 3 capacity, respectively. For loosening of the soil, the traditional Ethiopian ox drawn plow Maresha was used, the soil was then removed by ox-drawn scoops with a capacity of 0.13 m 3. The construction involved 140 oxen in one association and 90 oxen in the other, thus using a great part of the farmers and oxen available in the Peasant Associations. The experiences from these community works show that the construction of water harvesting structures is viable using draught animal power. Due to the changed socio-political situation, concerning land ownership and Peasant Associations, it is doubtful that works of this size can still be implemented. Therefore it is suggested to limit the number of farmers involved in the construction to a maximum of 30, all of whom should benefit from the ponds and be placed not more than one kilometre away. The capacity of the ponds should be reduced to 1,500 3,000 m 3, reflecting the decrease in available human and animal power involved in the construction. The farmers are expected to benefit in multiple ways from the pond construction: improved availability and accessibility of water, improved crop and livestock production, work and time used for water transport reduced. Introduction Water is a scarce resource in most parts of rural Ethiopia during the nine months dry period which extends from October to May. Both people and their livestock commonly travel long distances daily to obtain the water they need thus impairing agricultural productivity. Existing water supplies can be supplemented by improving water collection at spring sites, by constructing wells to tap group water supplies or by harvesting runoff water with excavated ponds or dams 1. Constructing ponds or dams using manual labour has been found to labour intensive with social consequences of not benefiting all who participated in the construction. The use of heavy machinery for construction of ponds or dams is expensive and difficult to sustain in a country like Ethiopia which has very limited foreign exchange for buying parts and fuel for running the machinery. An alternative of using ox-drawn scoops for excavating ponds has been developed and tested on-farm around the Debre Berhan area (Astatke and Saleem, 1996), about 130 km north of Addis Ababa. The 2001 published document on Rural development policies, strategies and instruments (Ministry of Information, 2001) states that without water agriculture is unthinkable. It is only when agricultural products get sufficient water at the right time that agri- 1 Even though the ratio of water stored for the amount of soil excavated is high in dams, the construction of dams implies the storage of water above ground behind a properly compacted embankment. As dams require proper design and water for the compaction of the embankments, they could not be totally managed by rural communities. 1

2 culture can be effective. If the supply of water is higher or less than the required amount or if it is not available at the right time, production could significantly decrease or even be zero. Therefore, in order to ensure rapid and sustainable agricultural development, there should be a reliable supply of water and appropriate or sustainable water management systems. If people engaged in agriculture get a sufficient amount of water supply throughout the year, it is possible to harvest higher yields on a smaller size of land and keep labour busy on production throughout the year. This is what should be set as a goal. The same document explains that although having policies and laws for water use is of paramount importance, without building a capacity to catch water and manage it, it will remain to be just a futile exercise. Because we have not built the capacity to control and manage the surface and ground water of our country, in places where there is high endowment of water, our people suffer from shortage of water and are forced to move from place to place following the tails of their animals in a very backward husbandry system and thus live in sever poverty. In places where uninterrupted sufficient amount of rain is available, we do not get economic benefits as much as we should because of failures to work throughout the year. To get a yield, even once a year, sometimes there will be untimely and too much rain and at other times it will be too short causing production to highly fluctuate from year to year. Our people are exposed to severe hunger due to the alarmingly erratic and short rainfall.. The Technology The major contribution of cattle to the agricultural production in the Ethiopia is through the draught power provided by oxen. Ethiopia presently has the largest draught oxen population in sub-saharan Africa with some 14 million oxen routinely used for cultivation (Worldbank, 2003). However, these oxen only work for about 60 days a year and the rest of the time they are not used for productive agricultural purposes (Gryseels and Anderson, 1983). The annual working cycle of an ox is characterized by short periods of high intensive labour and long periods of idleness, with about 15% of the feed intake actually used for work and the remainder being just dedicated to maintenance (Wilson, 2003). Considering that oxen have to be trained one year, the training starting at the age of two and that the working life lasts only about 4-5 years (Spiess, 1994), it is obvious that the farmers should try to diversify the use of the animals. Thus the high investments concerning training time and feed could bring better returns. Draught animals have been used for soil excavation and landscape shaping in some parts of the world. The basic scoop design employed in Ethiopia in 1983 was similar to the traditional Dutch mouldbaert and the British eighteenth century levelling box (Brandford, 1976). These European implements were designed to be drawn by large animals and so a smaller version with a capacity of 0.15 m 3 that could be pulled by a pair of Ethiopian zebu oxen was designed by staff of the International Livestock Centre for Africa (ILCA), ILRI s predecessor (Fig. 1). Initial testing of the technology began in 1983, with the excavation of a 7,000 m 3 pond on ILCA s previous, now the sheep research station of the Amhara Regional Agricultural Research Institute (ARARI) in Debre Berhan,120 km northeast of Addis Ababa. 2

3 Pond construction requires the use of two simple implements: the traditional cultivation implement the maresha and the animal drawn scoop as shown in Figures 1 and 3. The maresha is first used to break-up the soil surface where the pond is to be excavated. The loosened material is removed with the scoop to a dumping site at the end of the pond. The maresha is then used again to break-up the sub-soil which in turn is removed by the scoop. This pattern of tillage and scooping continues until the completion of the pond. The rate of scooping to tillage will depend on the size of the excavation to be made, the condition of the animals being used, the type and moisture content of the soil. For the onstation pond at Debre Berhan, approximately 10 hours of tillage were required for moving 100 m 3 of soil. Figure 1. Scoop design (Astatke et al., 1986) The problem that will be faced by the owners of the oxen is the extra feed required by their animals for the construction of the ponds. Most of the feed comes from the grazing of uncultivated areas or cereal straw stored after the cropping season. From the on-station work at Debre Berhan it was estimated that 11.20 MJ are required to excavate 1 m 3 of soil (Astatke, 1984). Since a kg of dry matter straw (straw has an average 10% moisture) contains about 6.5 MJ, the amount of hay required to excavate 1 m 3 of soil will be 1.83 kg for a pair of oxen. If the energy balance is done for the excavation of 7 m 3 of soil, an ox will have to be fed 7 kg of straw for the work (Astatke, 1984). This is similar to what farmers fed their oxen during the cultivation period (5 kg). The average draught power developed by a pair of local zebu oxen pulling a full scoop was 0.92 kw which falls within the upper range of the amount needed for the first pass 3

4 with the maresha (Astatke, 1984). Subsequently the Ethiopian Ministry of Agriculture (MoA) modified the scoop to reduce power requirements. New models with a 15 % capacity reduction compared to the first prototype and with two metal skids on the bottom to reduce friction were introduced and tested. Using these animal drawn scoops, two ponds of 9,500 and 8,700 m 3 capacities were constructed in 1985 by two Peasant Associations called at the time Kormargefia and Faji & Bokafia. Experiences of the two Peasant Associations in pond construction The work started in December 1984 and ended in March 1985. An inventory of working oxen showed that there were 148 and 93 pairs in the Kormargefia, and Faji & Bokafia Peasant Associations respectively at the start of the work. The oxen owners in each association were grouped by the location of their dwellings in relation to the pond sites. The numbers of oxen in each group were approximately the same. In Kormargefia, they formed seven groups with an average of 21 oxen pairs per group, while in Faji and Bokafia five groups were formed with an average of 18 pairs per group. A work programme for three months was then arranged by the Executive Committee of each Association for each group. In Kormargefia each group was scheduled to work once every nine or ten days while due to the lower number of oxen in Faji and Bokafia, each group was assigned to work once every six or seven days. Fines were set by each Peasant Association s Executive Committee for all absentees and un-punctual participants in the work. The pond at Kormargefia was constructed as a square with sides of 60 m while the Faji & Bokafia is rectangular with dimensions of 40 by 80 m. In both cases the oxen pulling the scoops entered the work sites from the higher end and dumped the excavated earth on the lower end. The soil dumping sites were 60 m and 80 m, the length of the pond sites for Kormargefia and Faji and Bokafia respectively, with a width of 20 m for both ponds. After dumping the soil the animals returned around the outer perimeter to re-enter on the upstream side for next cycle of excavation and dumping. Loosening of the ground surface to be excavated was done with the traditional cultivation implement, the maresha (Fig. 3). This was done in the same line as the direction of scooping to minimize cross-directional work going at the same time. One average the circuit length at the Kormargefia site was 140 m while that at Faji & Bokafia it was 200 m. The entry and exit slopes were approximately 1:3, while the other two sides had a slope of 1:1 (Fig 2). The estimated average quantity of soil excavated by a pair of oxen in one circuit was 0.13 m 3 (Figs. 4&5). The rate of work at both sites varied from day to day depending on the time worked, the conditions of the oxen pairs and the interest of the group on that day (Anderson and Astatke, 1985). Figure 2. Pond construction scheme 4

5 At the end of the work period in March 1985, the amount of soil excavated at Kormargefia and Faji & Bokafia sites were 9,500 m 3 and 8,700 m 3 respectively (Fig. 6). Farmers at Kormargefia site worked for 79 days on their pond in the period from December 1984 to March 1985 while farmers at Faji and Bokafia site worked a total of 76 days. The average length of a working day was 6.5 hours at Kormargefia while it 5.9 hours at Faji & Bokafia. At Kormargefia an average 3.1 oxen pairs per day were used to break the earth with a maresha prior to excavation and 15.2 oxen pairs per day were used with scoops for excavation. The corresponding numbers at Faji & Bokafia were 2.8 and 13.7 respectively. The net excavation rate per oxen pair per day, including oxen involved in both ploughing and scooping was 6.6 m 3 at Kormargefia and 7.0 m 3 at Faji & Bokafia (Anderson and Astatke, 1985). The oxen used at both sites were in good condition throughout the working period. All farmers were also able to handle the scoops properly by the end of their first working day. A few breakages of scoop handles occurred during the first week of work while the oxen were being trained. The broken handles were replaced by the farmers. Figure 3. Loosening of the soil with the maresha with scoops working in the background Figure 4. Group of farmers working on pond excavation 5

6 Figure 5. Dumping of soil from scoop Figure 6. Finished pond at Kormargefia Peasant Association Conditions suggested for the use of animal power in pond construction under current conditions The experience of the two PAs, Kormargefia and Faji & Bokafia, show that technically there are no problems in using animal power for the construction of ponds. The scoops also proved to be robust and practical and the current costs are estimated to be between 250-300 Birr per scoop. Even though rents for a pair of oxen with the handler have risen to 30-40 Birr/day (Spiess, 1994) in the last 20 years, thus raising the excavation rate to 5 Birr per m 3 of soil, it is still probably the cheapest means of soil excavation in the country at present. It is also means diversifying the power source available to farmers for other essential activities that would improve the livelihood of rural people. 6

7 However, the experience of the two PAs was during the socialist period (command system) where the Executive Committee exercised a lot of power. The Executive Committee selected the site and landownership being no factor as all land belonged to the government and the whole PA worked for the benefit of only a third of the community. Fines where set by the Executive Committee for absentees and farmers coming late for work on the ponds. Due to the socio-political changes within Ethiopia these conditions have changed, mainly concerning availability of common land. The authors of this paper strongly argue that if the social mechanisms are not properly set to fit the present situation, even though simple, the use of scoops for the construction of ponds will not work. If the social framework could be developed in a way that all participants in the community work benefit from its outputs, it will not only succeed but will facilitate in creating cheap and practical water conservation structures in the rural areas of Ethiopia. Some of the suggestions for the implementation of animal drawn scoops in the rural areas would be: water is a major constraint in the area and the communities are not only aware of it but are willing to alleviate the problem through their efforts clusters of 20-30 households will be taken as a unit for pond construction and usage the pond site selected should not be more than a kilometre from the furthest house in the unit in the unit of 30 households it is assumed that there will be more than 15 pairs of oxen and the community is willing to use them for pond excavation those who do not own oxen in the unit are willing to participate in other ways in the construction of the pond As the number of households will be limited to 30, the capacity of the pond would be reduced proportionally (1,500-3,000 m 3 ) as compared to the previously constructed ponds, depending on the purposes of the water use in the community the capacity of the pond would also determine the size of the area, in this case with an average area of 600 m 2 and an average pond depth of 3.5 m Implications There is a high potential for use of untapped animal power in Ethiopia based on the livestock population and that traditionally the draught oxen are only used for soil cultivation. Acceptance of the construction itself by the farmer community can be assumed as high, if the stakeholders are direct beneficiaries of the constructed ponds. The location of the pond will be a critical issue, as farm sizes tend to be small (around 2 ha) and farmers will be reluctant to part with their land if more people will be beneficiaries. The farmer groups will have to decide were to put the reservoirs and how to compensate lands that have been used for this purpose. 7

8 Benefits of pond construction: Water availability for households throughout the year Improved livestock production Time and labour for water transport reduced Higher water availability for vegetables and homegardens Improved hygiene due to better to access to water Potential for pisciculture (Tilapia) which is new in the farming systems Water harvesting and runoff reduction Animal power used not only for land preparation (better opportunity costs) Second harvest possible even without belg (short rainy season) rains Better recharge of groundwater and springs Additional water available for biogas production and other water related processes References Anderson, F. and Astatke, A. 1985. Pond Excavation using oxen-drawn scoops in rural Ethiopia. Report. Highlands Programme, ILCA, Addis Ababa, Ethiopia Astatke, A. and Saleem, M. 1996. Draught animal power for land-use intensification in the Ethiopian highlands. World animal review. Vol. 86. 1996-1. FAO, Rome. Astatke, A. Bunning, S. and Anderson, F. 1986. Building ponds with animal power in the Ethiopian highlands. A manual. ILRI, Addis Ababa, Ethiopia. Astatke, A. 1984. The use of animal power in water conservation works. M.Sc. Thesis Cranfield Institute of Technology. Silsoe College, Bedford, UK. Brandford, P.W. 1976. Old farm tools and machinery. David and Charles, Devon, UK. Gryseels, G. and Anderson, F. M. 1983. Research on farm and livestock productivity in the central Ethiopian highlands: Initial results, 1977 1980. Research Report 4, ILCA, Addis Ababa. Ministry of Information, 2001. REPUBLIC OF ETHIOPIA. RURAL DEVELOPMENT POLICIES, STRATEGIES AND INSTRUMENTS. Ministry of Information, Press and Audiovisual Department, November 2001. Addis Ababa, Ethiopia. Spiess, H. 1994. Report on draught animals under drought conditions in Central, Eastern and Southern zones of Region 1 (Tigray). UNITED NATIONS EMERGENCIES UNIT FOR ETHIOPIA, Addis Ababa, Ethiopia. Wilson, R. 2003. Effects of draught animal power on crops, livestock, people and the environment. In Proceedings: Responding to the increasing global demand for animal products. International Conference, 12-15 November 2002. University of Yucatan Cultural Centre, Merida, Mexico. Worldbank, 2003: Adoption patterns. Sub-Saharan Transport Policy Program (SSATP). Available at: http://www.worldbank.org/afr/ssatp/rttp/3_1challenges.htm. Last checked. 08.05.03 8