Ethiopia is a country of huge
bio-diversity and agricultural complexity. As in many developing countries,
agriculture plays a key role in Ethiopia's economy. It provides employment for
more than 80% of the population and contributes to nearly 50% of gross domestic
product.
The major crops produced include cereals, legumes, oil seeds,
roots and tubers, vegetables, fruit crops, coffee, spices and cotton. About 95%
of food production in Ethiopia comes from the peasant sector, where production
technologies are primarily traditional. Land holdings range between 0.5 and 3 ha
or less, depending on the geographical region of the country1. Land is prepared
for planting by oxen drawing a local plough (the maresha) or by manually
operated hand tools. Sowing is done by broadcasting and weeding is
dependent upon labour intensive practices. The use of irrigation, improved seed
and other external inputs such as pesticides is minimal.
Inter-cropping is a common practice. Patches of different
crops (cereals and legumes, cereals and oilseeds, cereals and cereals, cereals
and trees) are often grown side by side in the cereal-based systems of the
central and northern Ethiopian highlands. Cropping patterns in the root
crops-dominated southern Ethiopian highlands are characterised by even more
heterogeneity.
Pesticide research in Ethiopia
The importance of crop protection research has long
been recognised by the Ethiopian Agricultural Research and Extension System, and
research on pesticides was prominent, especially during the 1970s and
early 1980s. Concerted efforts on pesticide research in Ethiopia started in the
early 1970s. These included screening of insecticides, fungicides and
herbicides; recommendations on pesticide use were based on the results of
screening trials or on the basis of experience gained in neighbouring countries.
Some work on screening of rodenticides was also initiated around the mid 1970s
at the Holetta Research Centre of the Institute of Agricultural Research (IAR).
In general, pesticide research in Ethiopia concentrated on
synthetic pesticides; little emphasis, until recently, was given to research and
development on other groups of pesticides such as growth regulators, pheromones,
microbial control agents, and botanicals.
The IAR and academic institutions, are responsible for
conducting large and small scale screening trials to determine the efficacy of
various pesticides. The Desert Locust Control Organisation for Eastern Africa (DLCO-EA),
with its headquarters in Addis Ababa, also has its own pesticide importation and
testing protocol.
Pesticide regulation
Although there is legislation governing pesticide
registration, clear guidelines on the importation, testing, and use of
pesticides have not been enforced effectively. To date therefore it is not
uncommon for pesticides whose use is restricted in industrialised countries to
be widely used in Ethiopia. Furthermore, no pesticide has been officially banned
in this country although 16 African countries (Benin, Burkina Faso, Cameroon,
Chad, Egypt, Ivory Coast, Kenya, Madagascar, Mauritania, Mauritius, Mozambique,
South Africa, Sudan, Togo, Zambia and Zimbabwe) have officially restricted,
banned or withdrawn use of the Dirty Dozen pesticides (as outlined by the
Pesticides Action Network [PAN])2.
For example, DDT (a Dirty Dozen pesticide) is used in
Ethiopia for the control of the mosquito malaria vector and against agricultural
pests. World-wide DDT is banned in 49 countries. In Africa it is banned in
Benin, Burkina Faso, Cote d'Ivoire, Egypt, Madagascar, Mozambique, Togo and
Zimbabwe. Kenya, Mauritius, and South Africa have also restricted the use of
DDT3.
Recent action by the reactivated National Pesticide
Registration Committee has meant that 25 products (17 insecticides, 5 herbicides
and 3 fungicides) have been registered in Ethiopia.
| Pesticide formulation at Adami Tulu | ||
| Product | Formulation | Quantity pa |
|
endosulfan |
dust |
600 t |
|
DDT |
dust |
500 t |
|
malathion |
dust |
400 t |
|
endosulfan |
25% ULV* | 500 m3 |
|
endosulfan |
35% ULV |
250 m3 |
|
malathion |
50% EC** |
450 m3 |
|
dimethoate |
40% EC |
100 m3 |
|
dimethoate |
40% ULV |
100 m3 |
|
diazinon |
60% EC |
50 m3 |
|
fenitrothion |
50 EC | 50 m3 |
|
*
ULV = ultra low volume |
||
Pesticide formulations
At present, all agricultural pesticides used in
Ethiopia are imported. However, construction of a new pesticide formulation
plant has just been completed near the town of Adami Tulu in the Rift Valley,
some 170 km south of Addis Ababa. According to Mr. Makonnen Tessema, project
manager of the plant, it aims to produce liquid and dust formulations of the
insecticides shown in Table 1. It means that the full projected annual
production capacity of the formulation plant is about 3,000 tonnes. It is
expected that the plant will operate at 85% capacity during the first year and
100% in the third year.
Pesticide imports
Based on 1983-1993 figures, Ethiopia's annual import
of pesticides is estimated at more than 3,800 tonnes (figure 1), worth
approximately US$21 million4. In addition, the crop protection wing of the
Ministry of Agriculture receives (mainly as donations from the West) an average
of about 203 tonnes per annum for controlling the African armyworm and locusts.
About 72% of all pesticide imports are insecticides, 25% are herbicides, 2.6%
are fungicides and 1.3% others such as rodenticides, disinfectants.
Pesticide imports during the 1991 season almost collapsed
(figure 1) owing to the shortages of foreign exchange created by the previous
government that was in the process of being overthrown.
The state sector has been the major
user of pesticides in Ethiopia. Of the average 3,815 tonnes of pesticides
imported between 1983 and 1993, the former Ministry of State Farms Development (MSFD)
accounted for more than 37% (or nearly 1,350 tonnes), with the Ethiopian Seed
Enterprise (ESE) and the Ethiopian Grain Enterprise EGTE) sharing roughly 1.6%
(or 57 tonnes) and 0.1% (3 tonnes) respectively. About 70% of all pesticides
used by MSFD are insecticides, with herbicides (22.5%), fungicides (7%) and
rodenticides (0.7%).

Obsolete pesticide stocks
One of the major problems associated with pesticides
is their disposal. Developing countries are often handicapped by the lack of
trained personnel, facilities and funds to get rid of obsolete pesticides. As of
May 19926 the total pesticide stocks in Ethiopia amounted to nearly 5,400 tonnes
(insecticides 75%, herbicides 14%, fungicides 10% and others 1%) distributed
among MOA (47.6%), MSFD (42.8%), the former Ministry of Coffee and Tea
Development (5.5%) and the DLCO-EA (3.6%). Included in this stock are 652 tonnes
of Dirty Dozen pesticides mainly DDT, lindane, heptachlor, aldrin, chlordane,
paraquat7.
The magnitude of pest problems
A large number of insect pests have been recorded on
major crops in Ethiopia, but only a few of these are considered to be of
economic importance. Examples include stalk borers on maize and sorghum;
grasshoppers on small cereals; bean stem maggots on haricot beans; fruitworms
and tobacco whitefly on vegetables; scale insects on citrus; and bollworms on
cotton8.
Crop yield losses due to pests and
diseases in Ethiopia and elsewhere in Africa stand at 30-40%. Data on yield
losses caused by insect pests in Ethiopia range anywhere between 0 and 100% and
average: cereals 32-60%; pulses 19-63%; vegetables 24-49%; citrus 2-9%; and
cotton 36-60%9.
Crop loss significance
Although the losses quoted are useful as indicators of
the potential ability of a particular pest under the worst case scenario, they
should be interpreted with great caution10,11.
Firstly, most yield estimates are obtained from on-station
experiments and therefore do not represent normal farm practices and cropping
systems of the farmer.
Secondly, such experiments are conducted in an artificial
environment with increased pest pressure. For example, planting is synchronised
with periods of peak pest population. Susceptible cultivars are usually employed
as a test crop, and only mono-cropping is used. All of these factors
under-estimate the ingenuity and accumulated knowledge of the farmer. The farmer
is aware of when to plant his/her crop cultivars which are not as susceptible to
pests and diseases. Most cropping systems under small-scale production are also
rarely mono-crops either in time or space.
Thirdly, most if not all, figures are obtained from limited
areas and it is inaccurate to extrapolate information gathered at a specific
location to the national or regional situation.
Finally, the yield loss estimates do not take into account
contributions of factors such as vegetation diversity and edaphic (soil) and
climatic conditions. Crops in Ethiopia are grown under diverse vegetation
conditions which may have profound effects on arthropod pest and natural enemy
populations, In general, pests in diverse cropping systems become significant
only when the proper cultural practices are not followed. For instance, the
maize stalk (Busseola fusca), is considered a major pest of maize and
sorghum in many parts of Ethiopia and elsewhere in the eastern Africa region.
However, the work of Gebre-Amlak et al12 demonstrates that adjusting planting
date alone can result in little or no yield loss. Yield loss figures between
insecticide treated and untreated plots sown between early April and beginning
of May (as practised by farmers) are insignificant. By contrast differences were
observed in plots sown later than early May.
The complex agricultural systems that dominate the farming
systems in Ethiopia encourage natural enemies and hence natural biological
control. Therefore pest outbreaks of the magnitude seen in commercial
agriculture do not occur under traditional farming systems (with the exception
of migratory pests such as the African armyworm or locusts).
All these factors mean there is a strong justification for
not needing pest control measures in smallholder agriculture, as long as the
traditional holistic technique is not disrupted by agricultural development
initiatives that do not compensate for such complex systems.
Conclusion
Production in smallholder agriculture is characterised
by a high degree of agricultural and biological complexity. Such diversity
means that pest and disease outbreaks on the magnitude experienced in commercial
agriculture are rare (with the exception of migratory pests). Pesticide use in
such circumstances is therefore uncommon. Current initiatives by the Ethiopian
government to bring about food self-sufficiency and increased security may
maximise the diversity, by way of agricultural intensification and
extensification. This is expected to result in increased demand for pest control
management. Pressure by interest groups supporting pesticide sales will also
increase and farmers may then be persuaded that pesticide use is the only way to
reduce crop losses due to pests and diseases. Research should be able to provide
alternatives to pesticides; the basis for this will be understanding how
traditional pest management strategies operate.
Economic and environmental concerns about pesticides make
them unsuitable for use in smallholder agriculture and therefore pest management
in Ethiopian food crops will rely on an IPM approach that will maximise
cultural practices, natural biological control, and use of host plant
resistance. Pesticides may constitute an important component of IPM in high
value crops in commercial agriculture. Research focus under such circumstances
would be on pesticides that are compatible with IPM programmes.
References
1. Stroud, A. and Mekuria, M., Ethiopia's agricultural sector: an overview, In: Franzel S, van Houten H (eds), Research with farmers: lessons from Ethiopia, CABI, Walingford, UK, 1992, pp9-27.
2. PAN, Demise of the dirty dozen, Global Pesticide Campaigner, 1995, 5(3): 12-13.
3. Ibid.
4. Gordon H., Chiri A. and Abate T., Environmental and economic review of crop protection and pesticide use in Ethiopia. Winrock International Environmental Alliance, US, 1995, 117pp.
5. Abate T., Ampofo, J.K.O., Insect pests of beans in Africa: their ecology and management, Annual review of Entomology, 1996, 41:45-73.
6. Central Statistics Authority, Agricultural sample survey 1994/95, report on agricultural practices (private peasant holdings, main season), 1995, Vol. 3, Statistical Bulletin, 132, CSA, Addis Ababa.
7. Food production, food security and nutrition: subprogramme 4: pre and post harvest losses, October 1993, Addis Ababa.
8. Abate T., Integrated pest management in Ethiopia: an overview, At: workshop on IPM in smallholder agriculture, 9-13/10/95, CTA/IAR, Addis Ababa.
9. Ibid.
10. Op. cit. 8.
11. Op. cit. 5.
12. Gebre-Amlak A, Sigvald R, Pettersson J, The relationship between sowing dates and maize stalk borer, Busseola fusca (Fuller), infestation and damage on maize in Awassa, Ethiopia, Tropical Pest Management, 1989, 36:279-281.
13. Op. cit. 4.
14. Ibid.
Tsedeke Abate is an agronomist at the Institute of Agricultural Research, Nazareth Research Centre, Ethiopia.
[This
article first appeared in Pesticides News No. 33 as part of
the Focus on Food supplement, September 1996,
pages 12-13]