Water hyacinth (Eichhornia crassipes (Mart.): Land use/land cover changes and community-based management in east Shoa zone, Ethiopia
Abstract
Water hyacinth was officially reported in Ethiopia in 1956 at Koka Dam and Awash River and it is considered as a constraint to the development of the country. Thus, this study was undertaken to determine Water hyacinth and associated land cover/use changes, and capture perceptions regarding community-based management to enhance its proper control/eradication in Lume and Boa districts, east Shoa zone, Ethiopia using integrated approach. The method of study included Water hyacinth and associated land use/cover change analyses, focus group discussions, discussions with experts at the district, zone and region levels and undertaking consultative workshop. The land use/land cover change analyses revealed increased area coverage by Water hyacinth from about 145.53 ha in 1986 to 2319.48 ha in 2015 with decline in the area of water bodies and wetlands. The annual rate of increase in the area of the weed was about 51.51% while water bodies and wetlands declined by about 0.49% and 1.16%, respectively. Of the 10 group discussions undertaken in the study districts with the communities, 9 of them reported water hyacinth to increase in terms of area coverage since its appearance in their areas which concurs the results obtained from satellite image analyses and they reported the weed to be very harmful to their livelihood. Furthermore, the nine group discussants disclosed water hyacinth to be of no use to them. Recommendations included developing comprehensive management strategies and action plans, analysis and defining roles of each stakeholder, awareness creation, training, institutional linkages, co-management and reduction of nutrient load in water bodies.
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Introduction
Water hyacinth, Eichhornia crassipes (Martius) Solms- Laubach, is fast growing aquatic free floating fresh water plant indigenous to Brazil, Amazon basin and Ecuador region [1]. It was introduced as an ornamental species to adorn the water bodies in many countries more than a century ago for their attractive blue or purple flowers, oblong to oval glossy leaves with bulbous petioles. Later, this supposed-to-be prized plant was discovered to be an invasive species and posed serious socioeconomic and environmental problems affecting millions of people in riparian communities [2]. The sturdy plant has emerged as a major weed interfering with anthropogenic activities and is recognized as one of the top 10 worst weeds in the world [3].
In Ethiopia, water hyacinth was first reported in Lake Koka in 1956, the Awash River and since then, it has been found in different regions of Ethiopia. It is considered as a constraint to the development of the country [4] which has multifaceted problems such as obstructing electricity generation, irrigation, navigation, and fishing; increasing evapo-transpiration resulting in water loss, increase cost of crop production, providing habitat for vectors of malaria and bilharzias, harbors poisonous snakes, causing skin rashes, and hosting agents of amoebic dysentery and typhoid [4, 5] [5] and these effects have also been documented elsewhere in the world [2, 3]. The weed has infested water bodies in the two intervention districts (Lume and Bora) of the Livestock and Irrigation Value Chain for Ethiopian smallholders (LIVES) project in east Shoa zone of Oromia Region and with connection to the Awash River includes Koka Dam, lakes Ellen and Elletoke.
Local farmers in Bora district grow a number of crops for home consumption and sale mainly maize, wheat, haricot bean and tef (Eragrostis tef) while vegetable production (tomato, onion and others) is practiced along the shores of the lakes, mainly by private investors. Koka reservoir and lakes Ellen and Elletoke are the main water bodies in the district and are mainly used for irrigation and fishery. Koka dam is also used for recreation while the primary purpose is for hydro-electric power generation. Koka dam and the Awash River are also found in Lume district and their use is similar to that in Bora. Similar to Bora, the livelihood of farmers in Lume is based mainly on crop production which is followed by livestock production in the form of cattle, sheep, goats, chickens, and equines although the intensity of cropping is more in Lume than in Bora district.
The economic importance of these water bodies in the study districts for many families and nationally is significant [4]. However, the extent of land covered, the spatial and temporal cover changes of water hyacinth and associated land covers/uses is not documented although there is a growing global concern about land use/cover changes which emerged due to realization that changes of the land surface influences climate and impact on ecosystem goods and services [6]. Furthermore, despite the long history of this weed in the study districts and compared to complex and diverse nature of the problem, the interventions undertaken to control the weed particularly, in the open community field, does not much with its expansion which justifies the need to assess the possibility of applying community-based management (CBM).
The objectives of this paper were to determine water hyacinth and associated land cover/use changes over the past three decades (1986 to 2015) along water hyacinth infested water bodies and capture perceptions regarding CBM, to enhance proper control/eradication of the weed in Lume and Bora districts.
Conclusion
The results show that the extent of the problems in the study area vary from site to site requiring different approaches and use of different techniques for management of the weed, i.e., physical (manual and mechanical) and biological interventions in single or in combination depending on the nature and extent of the problem. Intensified monitoring, mitigation and management measures are needed to keep water hyacinth at unproblematic levels. For this to happen, it is very clear that the role of communities in control/eradication of water hyacinth should be increased through training, awareness creation, strengthening linkages, and supporting the communities by proving resources which are beyond their reach.
In view of the major findings of the study and the above conclusions, the following recommendations can be drawn:
- It is critical to develop comprehensive management strategies and action plans. A multidisciplinary approach should be designed, which ensures that the highest political and administrative levels recognize the potential seriousness of the weed. Solicit the good will of politicians to support water hyacinth control
- Plans should also state clearly the role of each government department, stakeholders, municipal councils and local community involved in the fight against water hyacinth
- Methods for water hyacinth control should include reduction of nutrient load in the water bodies through treatment of waters flowing from sewage works, urban wastes and factories. Changing land use practices in the riparian communities through watershed management will help reduce agricultural runoff as a mechanism for controlling the proliferation of water hyacinth
- Early detection and monitoring are critical for the management of water hyacinth, as successful eradication or containment is normally only possible when infestations are small. This is also essential to avoid re-establishment and further spread from the soil seed bank
- Education programs particularly public education and establishment of information center need to be undertaken