UNITED NATIONS
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Armyworm biology and ecology
The African armyworm (Figure 1) is not actually a worm at all but rather the larval (caterpillar) stage of the night flying moth, Spodoptera exempta. The normal seasonal cycle of the armyworm begins with low-density breeding in the cool, coastal highland of Kenya and Tanzania. These small populations of the "solitary" phase do little or no crop damage but as the Inter Tropical Convergence Zone (ITCZ) begins moving northward the strong winds carry the moths into the interior highlands where the initial outbreaks can occur. It is in these highland areas that a peculiar and not well-understood biological mechanism may occur whereby the solitary pest transforms into the 40 times more active gregarious form. The voracious appetite of this gregarious form is such that a heavy infestation can consume rangeland grasses or wheat, barley, teff, maize, sorghum or finger miller faster than 400 head of cattle per hectare and vast areas can be decimated overnight. |
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As noted above, the tracking of armyworm infestations is difficult as the moths are nocturnal and can move long distances with the seasonal winds. The most effective way of tracking/predicting armyworm infestations in through pheromone moth traps using a synthetic female hormone to attract males. The trapped male moths are counted each morning and when the count reaches 30 or more moths per day a light outbreak will be eminent within 7-10 days and the second generation outbreak (within about a month) can be severe. During severe outbreaks counts of several hundred moths are common. (In the 1994 armyworm outbreak in Ethiopia the pheromone trap at Asbe Teferi - West Hararghe - caught in excess of 1,000 moths every night between 23 and 29 May with a maximum catch of 1,923 moths in one night. This station continued to catch more than 100 moths per night until 7 July.)
Control measures
The very low densities but wide dispersal of armyworms in their initial breeding areas in Kenya and Tanzania make spraying operations uneconomical and, to a certain degree, control can only be initiated when there is a problem. The key to controlling armyworm infestations lies in the effective use of moth traps to predict infestations and, once infestations are noted, extremely quick interventions. The speed, wide dispersal and damage an armyworm infestation can cause are difficult to imagine and, once established, very difficult to control because there are sudden and urgent needs for control equipment and pesticides throughout a very large geographical area.The 1994 infestation is a prime example of speed and wide dispersal of armyworm infestations and even aerial spraying operations in 1994 could not keep pace with the new infestations being reported on a daily basis.
Local farmers are well aware of the dangers of armyworm infestations and will usually take immediate action on their own initiative. Warning of possible infestations may come from the radio or sudden swarms of moths around cooking fires or candles. Traditional control measures are usually practiced on rangelands and include driving herds of cattle, sheep and/or goats back and forth across affected areas, dragging thorn bushes or beating the infested areas with sticks and branches, collecting larvae by hand (often used on crop land) or letting chickens feed on larvae.
Although traditional control measures can be effective for small areas and pose no ecological dangers, they are limited value in areas of heavy infestation. (In 1994 the Western zone of Tigray reported 52,286 hectares affected of which 419 were controlled by traditional means involving 10,230 people while as much as 2,400 hectares were sprayed in a single day from the air.)
While aerial spraying can cover large tracks of land under the good conditions, effective spraying is logistically very complicated with extremely close coordination needed between ground staff to mark the affected areas, logistic support in terms of having the right amount and type of both aviation fuel and pesticides at the right airfield and regional authorities in terms of determining priorities. Aerial spraying can also be delayed or hampered by rain and fog, which if it continues for several days, may mean that spray materials and fuel will have to be re-positioned to another area. Lastly, aerial spraying can easily kill whole beehives, an important source of income for many rural families.
If equipment and pesticides can be in positioned quickly enough, the
most effective control measure seems to be motorized backpack sprayers
with ULV attachments. Hand-held battery operated ULV sprayers have also
been used extensively in Ethiopia but a large supply of batteries must
be assured if the operation is to be successful. (In 1994 the Government
of Ethiopia had to make an emergency purchased 50,000 dry cell batteries.
This purchase was in addition to extensive battery purchases made by CARE
for control operations in Hararghe a month earlier.)
1994 Armyworm outbreak in Ethiopia
The 1994 armyworm outbreak in Ethiopia was the most serious in the experience
of crop protection officials since 1984. From April to July, successive
generations of moths migrated northward with the ITCZ to cause widespread
and serious outbreaks on cereal crops in their early and most vulnerable
stage of development. In 1994, as is previous cases of armyworm outbreaks,
this outbreak followed a period of drought that exacerbated the economic
impact of the armyworm damage.
Region |
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Oromia |
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510,815
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SNNPR |
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50,000
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Somali Region |
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43,740
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Region 13 (Harer) |
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10,225
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Dire Dawa |
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4,675
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Amhara |
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159,815
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Tigray |
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40,402
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834,446
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Source of Funding |
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UNDP Emergency Fund (SPR) |
$ 50,000
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Consultant, aerial spraying & logistic support |
Government of Switzerland |
$ 38,000
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Aerial spraying and logistic support |
Government of Norway |
$ 6,500
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Logistic support |
Government of Netherlands |
$ 8,234
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Logistic support |
However as the infestations spread a major emergency control operation
became necessary and various emergency task forces were established to
assist the Government with control operations. In addition to direct contributions
from several donors to the MoA and/or DLCO in cash and in kind, the UN-EUE,
utilizing contributions from the UNDP Emergency Fund, and the Swiss, Norwegian
and Netherlands governments, worked very closely with the Plant Protection
Agency of the Ministry of Agriculture in organizing both emergency flights
of aviation fuel and pesticides to the north as well as funding aerial
spraying operations in Tigray. Total funds contributed to the UN-EUE intervention
are shown in Table 2.
On 10 July MoA reported 869,000 hectares affected with severe infestations in Tigray region with the first generation starting in early June and the second generation starting on 30 June with the level of infestation increasing in spite of ground and aerial spraying, which commenced on 28 June 1994.
By 21 July the situation was under control in the Western Zone of Tigray but there were reports of new outbreaks in 13 weredas (15,284 hectares) of the Eastern Zone and 17 weredas (25,790 hectares) of the Southern Zone. In order to meet this new crisis, additional flights of pesticides and avgas were organized.
Aerial spraying operations concluded in early August and in spite of
numerous logistic problems the overall operation was successful and estimated
crop losses in Tigray were only about 2,500 hectares that had to be re-planted.
However, in Oromia region the regional Agriculture Bureau reported armyworm
damage much higher than in Tigray with losses of some 26,000 M/T of sorghum
and 32,500 M/T of maize.
The 1996 outbreak
The 1996 armyworm outbreak was much less severe than the 1994 outbreak but nonetheless almost 250,000 hectares in seven regions were affected, of which about 200,000 hectares were cropland. Chemical control measures through manual and motorized backpack sprayers were applied to about 93,000 hectares at a cost of roughly US $ 650,000. Aerial spraying was not used in 1996 because ground application was generally sufficient. Although this outbreak was successfully controlled and, unlike 1994, only about 1,000 hectares had to be replanted, the 1996 outbreak raised a number of issues concerning both the early warning system and control operations and if the rains had not been both timely and heavy the infestation might have been as severe and 1994. Of particular concern were problems with the pheromone moth traps (lack of pheromone capsules, traps not operational or not "counted" and delays in reporting moth counts). Control operations also faced problems because of lack of vehicles and communications with central offices, delays in the arrival of pesticides and sprayers and insufficient trained manpower.
The 1999 outbreak
Large-scale armyworm outbreaks were reported in both Rwanda and Burundi
in late April 1999 but initial estimates of 100,000 hectares of cropland
and 400,000 hectares of pasture in Rwanda being infested were later significantly
reduced. However, in spite of heavy rains and rapid interventions from
the Government and FAO concerns remain that the next generation could re-infest
many areas. In mid May the Government of Kenya issued and armyworm alert
and by 19 May the Kenyan Minister of Agriculture reported that 100,000
hectares had been affected, including a large strip along the coast and
the Rift Valley and that the infestation was the worst since 1984. At the
same time armyworm infestations were also reported in Uganda while the
joint WFP, USAID, EC and SCF-UK Food Security Assessment Unit for Somalia
reported heavy infestations from Middle Juba, Lower Shabelle, Bakool and
Hiran regions.
Region | Zones | Weredas | PAs |
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Infested areas |
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Crop | Pasture | Litres | Kgs. | |||||
SNNPR | 4 | 25 | 229 | 15/04/99 | 24,302 | 4,613 | 7,682 | 4,712 |
Oromia | 5 | 41 | 424 | 18/04/99 | 125,396 | 97,487 | 14,069 | 2,103 |
Somali | 5 | N/A | N/A | 03/05/99 | 69,000 | 1,307 | 218 | |
Harar | N/A | N/A | 17 | 06/05/99 | 6,000 | N/A | 145 | 900 |
Dire Dawa | N/A | N/A | 12 | 12/05/99 | 500 | N/A | N/A | N/A |
Gambella | N/A | 5 | N/A | N/A | N/A | N/A | N/A | N/A |
Tigray | 1 | 1 | 1 | N/A | N/A | 2 | N/A | N/A |
TOTAL | 13 | 72 | 683 | 162,498 | 102,102 | 23,203 | 7,933 |
In Ethiopia, armyworm outbreaks were first reported in SNNPR (Southern Region) on 15 April with subsequent infestations reported in Oromia and the Somali National Regional State. The Somali Region in their Plan of Action of 19 May, reported 69,000 hectares of cropland in Jigjiga were infested with somewhat milder infestations in Kebre Biyah, Harshin, Moyale, Filtu, Fik, Awbere, Babile, Erer and Degeh Bur. This same report also requests in-kind or cash assistance from the international community for fuel, dry-cell batteries and miscellaneous expenses in order to undertake control operations without delay. Although the initial infestations in the Somali Region were serious, on the night of 19 May there was an exceptionally heavy rain in the Jigjiga area that, although causing some damage in the town, destroyed most of the armyworms.
A report prepared by FAO in Ethiopia on information supplied from the Crop Production and Protection Technology and Regulatory Department of the Ministry of Agriculture indicates that as of 20 May 162,498 hectares of cropland and 102,102 hectares of pasture were reported by various regions to be infested with armyworms. Control operations had already started in most of the affected regions and so far no serious crop damage had been reported. The Ministry of Agriculture also report that they have sufficient stocks of pesticide to deal with the current levels of infestation.
Although the situation seems to be under control at the moment, if weather
conditions remain favorable further infestations could take place in northern
Ethiopia and Eritrea. Also, as control measures in Somalia may be difficult,
re-infestation of Ethiopia from Somalia is also possible. Armyworm infestations
can devastate large tracks of cropland and prompt interventions are critical.
If the 1999 armyworm infestation becomes as severe as the 1994 outbreak
then additional donor assistance may be required.
ACKNOWLEDGEMENTS
All figures in this report have been
reproduced from the 1993 FAO publication "A Guide to Migrant Pest Management
in Africa", edited by Dr. Wolfgang F. Meinzingen (available from the UNDP-EUE
library)
DISCLAIMER
The designations employed and the presentation of material in this document do not imply the expression of any opinion whatsoever of the UN concerning the legal status of any country, territory, city or area of its authorities, or concerning the delimitation of its frontiers or boundaries.
27 May 1999
UN-EUE | Tel.: (251) (1) 51-10-28/29 |
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Addis Ababa, Ethiopia | Email: undp-eue@telecom.net.et |