Chagema Kedera and Benson Kuria
Kenya Plant Health Inspectorate Service, P.O. Box 49592, Nairobi, Kenya; e-mail: kephis@nbnet.co.ke
Kenya has had several invasions of alien species that have had negative impacts on biodiversity, agriculture and human development. Studies show that Kenya has been invaded by 34 species: 11 arthropods, ten microorganisms, nine plant species and four vertebrates. Management strategies have included quarantine measures for unintentional and intentional introductions, eradication, containment and control, monitoring and research, regional cooperation and public awareness. More cooperation, assistance and capacity building is required to effectively manage the problem of invasive species.
Kenya has experienced a number of biological invasions, some of which have had significant consequences on socio-economic status (Keil, 1988). Notable examples include the larger grain borer (Prostephanus truncatus) (Hodges et al., 1983; Muhihu and Kibata, 1985), the water hyacinth (Eichhornia crassipes) (Hill, Cock and Howard, 1999) and Prosopis spp. Available information on invasive species in the East African region shows that some 34 different species have invaded Kenya (Farrell, Kibata and Sutherland, 1995; Lyons, 2000; Kibata, G.N., pers. comm.). Table 1 lists these 11 arthropods, ten microorganisms, nine plants and four vertebrates, and outlines their impacts. Few of these species are under control, hence the concern. Various management strategies and activities have been used to address the problem of invasive alien species in Kenya.
To prevent the introduction of invasive alien species into Kenya, importation of any plant material is subject to strict specified conditions. The stipulated procedures ensure that enough information on the plant material is available to evaluate the pest risk of potential invasives. Plant quarantine restrictions are based on pest risk analysis and existing scientific knowledge on the distribution, biology and pests of the plant. Suitable regulations are enforced to facilitate the import and export of plant materials through the issuance of import permits and phytosanitary certificates. Legal authority is provided to allow for treatment or destruction of infested or infected plants or plant products.
Inspections are carried out at the entry points (i.e. international airport, sea ports and borders) to enforce quarantine measures. The border control points are located where there is a risk of entry of alien species (see figure 1). Most are located in the southern and western borders of Kenya because there is considerable trade and movement of plant materials between Kenya and Uganda and Tanzania. There is no significant movement of plant materials in most of Kenya’s northern and northeastern borders (i.e. from Ethiopia and Somalia). Most of this region is arid.
Table 1: Invasive species recorded in Kenya.
Species |
Year of arrival |
Impact on native plants, animals and ecosystems |
Impact on humans (livelihood, transport, health etc.) |
1. Arthropods |
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Larger grain borer |
1983 |
Pest of stored maize and cassava |
Heavy post-harvest losses in maize; trade restrictions |
Serpentine leafminer |
1976 |
Pest of many horticultural crops |
Crop losses and loss of overseas markets due to quarantine requirements |
Western flower thrips |
1989 |
Pest of many flower crops, pulses and horticultural crops |
Intensified use of pesticides; loss of crop and capital due to quarantine requirements |
Cypress aphid |
1991 |
Cypress trees decimated |
Degraded environment |
Russian aphid |
1995 |
Barley and wheat production reduced |
Less food, income available |
Cassava mealybug |
1989 |
Reduced cassava production |
Less food, income available |
Leucaena psyllid |
1992 |
Reduced fodder |
Loss of capital |
Citrus woolly whitefly |
1970s |
Reduced fruit production |
Loss of capital |
Purple tea mite |
1976 |
Reduction in tea leaf production |
Loss of capital |
Tomato russet mite |
1976 |
Reduced tomato production |
Loss of capital |
Louisiana crayfish |
1970 |
Reduction of flora and fauna, increased turbidity |
Harvested by man |
2. Micro-organisms |
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Crown gall |
1995 |
Reduced production in roses |
Loss of capital |
Black Sigatoka |
1988 |
Reduced banana production |
Less food, income available |
Panama disease Fusarium oxysporum f. sp. cubense |
1952 |
Reduced banana production |
Less food, income available |
Cassava mosaic disease ACMV
(UgV) |
1994 |
Reduced cassava production |
Less food, income available |
Maize streak disease (MSV) |
1936 |
Reduced maize production |
Less food, income |
Fruit and leaf spot |
1972 |
Reduced citrus production |
Less food, income |
Citrus greening disease (bacterial) |
1972 |
Reduced citrus production |
Less food, income |
Barley yellow dwarf virus (BYDV) |
1983 |
Reduced barley and wheat production |
Less food, income available |
Napier grass smut |
1992 |
Reduced fodder production |
Loss of capital |
Coffee berry disease |
1940 |
Reduced coffee production |
Loss of capital |
3. Plants |
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Water hyacinth |
1989 |
Serious |
Very serious |
Water fern |
1984 |
Serious |
Serious |
Prosopis spp. |
1983 |
Serious |
Serious |
Wild garlic |
1993 |
NA |
Serious to horticultural farmers |
Prickly pear |
1940s - 50s |
Out-competes native plants, precludes grazing and browsing near it |
Poisonous, spines dangerous |
Mexican marigold |
Unknown |
Minimal |
Increased weed eradication costs |
Lantana |
1950s |
Out-competes other vegetation |
Poisonous to livestock, habitat for tsetse flies |
Morning glory |
1960s |
Grows over and out-competes other plants |
Reduced pasture |
Eucalypt |
1939 - 45 |
Minimal, though some evidence it retards recruitment of native species |
None |
4. Vertebrates |
|||
Nile perch |
1960s |
Greatly reduced abundance of native cichlids |
Economic boost to fishers, reduced catch of smaller species |
House sparrow |
Early 1900s |
Displacing local sparrows |
Noisy, messes buildings with nests |
Lovebird |
19th century |
Competing with local species for nest holes |
Pests especially for cereals |
Indian house crow |
1947 |
Displacing native species, kills fruit bats |
Urban pest, damages crops, hazard at airport |
Fig. 1: Map of Kenya showing agroclimatic zones and points of entry where phytosanitary inspection is carried out.
Intentional introduction of alien species in Kenya has been done under authority of the Kenya Standing Technical Committee on Imports and Exports, which is a body that approves importation of restricted and new materials into the country. The committee operates under the Plant Protection Act (Cap 324) of the laws of Kenya.
Most of the deliberately introduced alien species are biocontrol agents. An appropriate risk analysis is carried out as part of the authorization process before coming to a decision on whether or not to authorize a proposed introduction. A comprehensive dossier on the intended introduction is submitted for evaluation by the standing technical committee. Authorization of an introduction is accompanied by conditions such as containment requirements, monitoring procedures, preparation of mitigation plans.
For invasive species that have been unintentionally introduced to Kenya, appropriate steps such as eradication, containment and control have been undertaken to mitigate adverse effects. For instance, for water hyacinth control, options have included mechanical removal of the weed and the use of biocontrol agents. Enforcement of domestic quarantine has been done, such as when the larger grain borer was first detected. Monitoring was also carried out in other susceptible areas to detect invasion and hence put in place appropriate control measures.
Much research has been undertaken in Kenya to develop an adequate knowledge base to address the problem of invasive species (Farrell, Kibata and Sutherland, 1995). This has been especially so for serious invasive species such as the larger grain borer, the water hyacinth and Prosopis spp. Research has been undertaken by national research institutes such as the Kenya Agricultural Research Institute and Kenya Forestry Research Institute. Studies have included the biology and ecology of the invasive species (Nang’ayo et al., 1993), history and ecology of invasion and associated impacts on the ecosystem, species and socio-economic impacts. The Kenya Plant Health Inspectorate Service (KEPHIS), as the national plant protection organization in Kenya, has worked closely with the research institutions to determine the status of invasive species and develop management options.
Monitoring has also been done to detect new invasive species. Monitoring has involved institutions such as Kenya Agricultural Research Institute, the International Centre of Insect Physiology and Ecology and KEPHIS. Monitoring has been carried out for species such as larger grain borer, fruit flies and water hyacinth. Quarantine surveillance has also been done to detect new species.
There is a need for a regional approach to address the issue of invasive species because some of the species affect different countries. Examples include the water hyacinth, which has affected Kenya, Tanzania and Uganda, and the larger grain borer, which has severely affected Kenya and Tanzania (Hodges et al., 1983). To this end, there has been a move towards regional cooperation between the three East African states and harmonization of phytosanitary measures among the different countries. Strengthening of phytosanitary services, inspection and certification has also been done. This has played a big role in the prevention and control of invasive species.
On the international front, Kenya is a contracting party to the International Plant Protection Convention, whose purpose is to secure a common and effective action to prevent the spread and introduction of pests of plants and to promote appropriate measures for their control.
With assistance from the Food and Agriculture Organization of the United Nations, training of staff has been undertaken to make Officers aware of contemporary phytosanitary issues and ensure that they effectively implement phytosanitary measures. Staff have also been trained on specific phytosanitary issues such as pest risk analysis and identification of pests of quarantine importance.
Additionally, efforts have been made to strengthen phytosanitary activities within KEPHIS. These have included:
KEPHIS has striven to raise public awareness on phytosanitary issues and invasive species. This has been important in preventing the introduction and management of invasive species. Public awareness activities have included:
Kenya, like many other countries, is faced with the problem of managing invasive species that have caused socio-economic losses. The country has put in place several measures to mitigate the impacts of the invasive species. However, more cooperation, capacity building and assistance is needed to manage effectively the problem of invasive alien species.
References
Farrell, G., Kibata, G.N. & Sutherland, J.A., eds. 1995. A review of crop protection research in Kenya. KARI/ODA Crop Protection Project. Nairobi, Kenya, Kenya Agricultural Research Institute. 165 pp.
Hill, G., Cock, M., & Howard, G. 1999. Water hyacinth, its control and utilisation: a global review. CABI Bioscience and IUCN. Publications on Water Resources: No. 15. Stockholm, Sweden, Swedish International Development Cooperation Agency (SIDA). 54 pp.
Hodges, R.J., Dunstan, W.R., Magazini, I.A. & Golob, P. 1983. An outbreak of Prostephanus truncatus (Horn) (Coleoptera: Bostrichidae) in East Africa. Protection Ecology, 5: 183 - 194.
Keil, H. 1988. Losses caused by the larger grain borer in farm stored maize. In: G.G.M. Schulten & A.J. Toet, eds. Workshop on the containment and control of the larger grain borer, Arusha, Tanzania, 16-21 May 1988, pp 28 - 52. Rome, Italy, FAO. ii + 209 pp.
Lyons, E.E. 2000. Preliminary survey of invasive species in Eastern Africa. In: E.E. Lyons & S.E. Miller, eds. Invasive species in Eastern Africa: Proceedings of a workshop held at ICIPE, July 5 - 6, 1999, pp. 65 - 70. Nairobi, Kenya, International Centre of Insect Physiology and Ecology (ICIPE) Science Press. 108 pp.
Muhihu, S.K. & Kibata, G.N. 1985. Developing a control programme to combat an outbreak of Prostephanus truncatus Horn (Coleoptera: Bostrichidae) in Kenya. Tropical Science, 25: 239 - 248.
Nang’ayo, F.L.O., Hill, M.G., Chandi, E.A., Chiro, C.T., Nzeve, D.N. & Obiero, J. 1993. The natural environment as a reservoir for the larger grain borer Prostephanus truncatus (Horn) (Coleoptera: Bostrichidae) in Kenya. African Crop Science Journal, 1: 39 - 47.