ISSN: 2150-3508
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Review Article - (2021)Volume 12, Issue 3
The purpose of this review article is to explore the fishery resources, potentials, conservation challenges, and management strategies of Ethiopian water bodies. Ethiopia is one of the landlocked countries in the horn of Africa characterized with a wide range of ecological, geographical, edaphic, and climatic conditions that account for a wide diversity of its biological resources both in terms of flora and fauna. It has a high diversity of Ichthyologic Fauna, accounts for over 200 fish species. In average, the production potential yield of Ethiopia is accounted for 94,500 tons per annum in different water bodies. However, the actual production is 38,370, still far below the estimated potential yield. The main factors contributed to low production of fish including illegal fishing activities, lack of awareness, overfishing, wetland degradation, deforestation, invasive species, lack of infrastructure, and technologies. Capacity building towards aquatic policies, legislation and regulation, community empowerment, pollution control, invasive alien species control, threatened species conservation, integrated watershed management plan, illegal fishing, area and seasonal closure, and public awareness creation is needed to save the water bodies and to increase fishery production.
Challenge; Conservation; Ethiopia; Diversity; Fish resource; Management
Ethiopia is a land-locked country in the horn of Africa gifted with numerous aquatic resources, including over 20 natural lakes, 12 large river basins, over 75 wetlands, and 15 reservoirs [1]. Micro and macro dam construction and river impoundment have created innumerable large and small water bodies stocked with fish for fisheries [2]. Both inland capture fisheries and aquaculture activities are concentrated around the many lakes and rivers in the Rift Valley, as well as around the Blue Nile, which supplies water to the country’s largest water body. The inland water bodies cover approximately 7,400 km2 and there are 7,185 km of rivers [2,3]. Hence, the country is rich in fish diversity and abundance. Ethiopia also characterized by a wide range of ecological, edaphic, and climatic conditions that account for a wide diversity of its biological resources both in terms of flora and fauna [4]. The major geographic features are massive highlands, mountain, and plateaux divided by the Great Rift Valley and surrounded by lowlands along the periphery [5]. Those natural factors described above powerfully influenced Ethiopia’s extraordinary range of terrestrial and aquatic ecosystems and contributed to be endowed with a high diversity and rate of endemism [6]. Fisheries resource in Ethiopia, in spite of its significant contribution to poverty alleviation and food security, is an unexploited natural resource [7]. In average, Ethiopia can produce over 94,500 tons of fish per annum in different water bodies [8]. However, the country inadequate in food security and the economic growth is minimum, due to lack of technologies capable of resolving the problems of fisheries production. In worldwide, there are different threats of lakes include; accelerated Eutrophication, invasive species, toxic contamination, overfishing, water diversion, acidification, and climate change [9]. However, major conservation challenges of fish and fisheries in water bodies of Ethiopia are suffered from anthropogenic activities, illegal fishing activities like using narrow mesh size nets and poisonous plant seeds that cause toxic to the fish, lack of awareness of the community in fisheries management,no fish stock assessment has been done so far, limited institutional, technical and financial capacity and low research and development capacities, overfishing, wetland degradation, Dam construction for hydropower and irrigation, deforestation , urbanization and industrialization [2,10]. Therefore, the aim of this paper is to review fishery resources in different water bodies, conservation challenges and fishery management strategies in Ethiopia.
Ethiopia is endowed with several water bodies (lakes, rivers, streams, reservoirs, and substantial wetlands), consequently it contains a high diversity of Ichthyologic Fauna [8,11,12]. Froese and pauly list 175 species occurring in Ethiopia included six subspecies and ten introduced species [13]. This checklist was based on incomplete literature data which is not fully updated and sometimes erroneous which makes it questionable and dubious. However, the new modified checklist stated that there are 200 fish species in freshwater bodies of Ethiopia, which belong to 75 genera, 31 families, and 12 orders (Table 1) [14].
Order | Family | Genera | Species |
---|---|---|---|
Ceratodontiformes | Protopteridae | 1 | 1 |
Polypteriformes | Polypteridae | 1 | 3 |
Anguilliformes | Anguillidae | 1 | 1 |
Osteoglossiformes | Osteoglossidae | 1 | 1 |
Notopteridae | 1 | 1 | |
Gymnarchidae | 1 | 1 | |
Mormyridae | 8 | 16 | |
Gonorynchiformes | Kneriidae | 1 | 1 |
Characiformes | Alestiidae | 4 | 11 |
Distichodontidae | 5 | 9 | |
Citharinidae | 1 | 2 | |
Cypriniformes | Cyprinidae | 9 | 69 |
Balitoridae | 1 | 1 | |
Siluriformes | Auchenoglanididae | 1 | 2 |
Bagrida | 1 | 3 | |
Claroteidae | 2 | 3 | |
Schilbeidae | 4 | 6 | |
Amphiliidae | 3 | 3 | |
Clariidae | 2 | 5 | |
Malapteruridae | 1 | 2 | |
Mochokidae | 5 | 18 | |
Cyprinodontiformes | Cyprinodontidae | 1 | 2 |
Poeciliidae | 1 | 7 | |
Nothobranchiidae | 2 | 6 | |
Perciformes | Channidae | 1 | 1 |
Latidae | 1 | 3 | |
Anabantidae | 2 | 3 | |
Cichlidae | 6 | 11 | |
Gobiidae | 1 | 1 | |
Tetraodontiformes | Tetraodontidae | 1 | 1 |
Total | 70 | 194 |
Table 1: List of native fish species in Ethiopia [14].
From the total number of fish species, 194 are native, 40 are endemic, and 6 are exotic species. Three of the introduced species (ctenopharyngodon, idella, Esox lucius, and Hypophthalmichthys molitrix) apparently did not establish as self-sustaining populations in natural waters after their introduction and are not included in the checklist (Table 2).The distribution of fish species and overall diversity within the drainage systems is extremely uneven [8]. For example, in the Rift Valley, fish diversity is highest in its southern part, lowest in the central part, and intermediate in the northern part. The highest fish species of two diversities in Ethiopia has been recorded from Baro basin, followed by Abay, Wabishebele, and Omo-Gibe basins. However, endemicity seems to be highest in Abay and Awashbasins. This is attributed, in the former case, to the endemic species flock of Labeo barbus in Lake Tana (Table 3) [15].
Family | Species |
---|---|
Distichodontidae | Nannaethiops bleheri |
Cyprinidae | Barbus spec.''Bale'' |
Barbus arambourgi | |
Barbus spec.''Abaya'' | |
Barbus tanapelagius | |
Labeobarbus acutirostris | |
Labeobarbus brevicephalus | |
Labeobarbus crassibarbis | |
Labeobarbus dainellii | |
Labeobarbus gorgorensis | |
Labeobarbus gorguari | |
Labeobarbus longissimus | |
Labeobarbus macrophtalmus | |
Labeobarbus megastoma | |
Labeobarbus nedgia | |
Labeobarbus osseensis | |
Labeobarbus platydorsus | |
Labeobarbus surkis | |
Labeobarbus truttiformis | |
Labeobarbus tsanensis | |
Labeobarbus ethiopicus | |
Labeobarbus spec 'Genale' | |
Labeobarbus microterolepis | |
Labeo boulengeri | |
Garra aethiopica | |
Garra duobarbis | |
Garra geba | |
Garra igenestii | |
Garra makiinesis | |
Garra regrusses | |
Garra tana | |
Garra chebera | |
Narichorinus beso | |
Varicorhinus jubae | |
Balitoriidae | Afronemacheilus abyssinicus |
Amphiliidae | Amphilius lampei |
Phractura spec. ''Alvero and Bonga'' | |
Mochokidae | Chiloglanis modjensis |
Cyprinodontidae | Lebias stiassney |
Cichlidae | Danakilia franchettii |
Table 2: List of endemic fishes in Ethiopia [14].
Family | Species | Status |
---|---|---|
Salmonidae | Salmo trutta | Established |
Oncorhynchus mykiss | Established | |
Cyprinidae | Cyprinus carpio | Established |
Carassius auratus | Established | |
Ctenopharyngodon idella | ||
Hypophthalmichthys molitrix | ||
Cichilidae | Tilapia zilli | Established |
Tilapia rendallii | Not certain | |
Esocidae | Esox lucius | |
Pociilidae | Gambusia holubrooki | Established |
Table 3: List of exotic species in Ethiopia [14].
Fish has historically played an important role in food security in many countries and contributes to do so globally [7]. It provides 15% to 20% of animal proteins [16]. In Ethiopia, fish comes exclusively from inland water bodies including lakes, rivers, streams, reservoirs, and substantial wetlands that are of great socio-economic, ecological, and scientific importance [11]. Most of the information in much of the literature on the fish production potential of the country is not consistent, it contradicts each other. The majority of the estimates did not include the potential of small water bodies and in some cases even the rivers were not considered. However, Small water bodies are important for a number of reasons and could be a potential source of protein [8]. The overall potential yield of fish in Ethiopia water bodies is estimated as 94,500 tons per year (Table 4) on average. In an average, 73,100 tons per year (3.3%) for lentic (lakes, reservoirs, and small water bodies) and about 21,400 tons per year (11.9%) for the lotic ecosystems (riverine fishery). Lotic ecosystem is higher produced about 83% than previous estimates due to the larger number of water bodies considered, including the newly constructed reservoirs for irrigation development and hydropower generation [8].
Water bodies type | Area (km2) | Length (km) | Fish potential yield (ton/year) | Mean (tone/year) |
---|---|---|---|---|
Major lakes | 7,740 | 37,346-41,177 | 39,262 | |
Major reservoirs and dams | 1,447 | 7,698-8,059 | 7,879 | |
Small water bodies | 4,450 | 25,678-26,314 | 25,996 | |
Rivers | 8,065 | 18,855-23,954 | 21,405 | |
Total | 13,637 | 8,065 | 89,577-99,504 | 94,541 |
Table 4: Summary of fish production potential estimates of different water bodies in Ethiopia [8].
Even though the overall potential yield of fish in Ethiopia is high, the actual fishery production is far from the estimated [17]. The actual exploitation of fish production is 38,370 ton/year [18]. The current fish production is still far below the estimated potential yield [7]. This is might due to several factors. Lack of technologies capable of resolving the problems of fisheries production [8], habitat degradation, and destruction are the main causes of fish stock depletion of freshwater fishes and this why fish population differs per water body, even from habitat to habitat (Figure 1) [19].
Figure 1: The annual mean fish production potential estimates of different water bodies in Ethiopia (tone/year).
There are many rivers and lake available in Ethiopia which used for fish production, but there is still a problem regarding fish production and productivity to increase the profit of private and GDP of the country [7]. The overall potential yield of fish in Ethiopia water bodies is estimated as 94,500 tons per year on average [8]. However, the currently annual production is 38,370 ton/year [18]. This is low level of fish production may be attributed to the traditional fishing methods and equipment being utilized by the fishers. Similarly, Assefa, et al. lack of modern fishing tools and illegal fishing gears are also the challenges of fisheries of South Wollo Lakes of Ethiopia [20]. In addition to this, inefficient fishing gear, lack of motorized boat service, poor transportation access, lack of value adding facilities, lack of fish handling facilities (like refrigerator), poor postharvest handling and gear theft are the main constraints to fish production in different regions of Ethiopia [21,22]. In general, the Ethiopian fishery is under several constraints due to different challenges [7,23]. The major conservation challenges of fish and fisheries in water bodies of Ethiopia are suffered from anthropogenic activities, illegal fishing activities like using narrow mesh size nets and poisonous plant seeds that cause toxic to the fish, lack of awareness of the community in fisheries management, no fish stock assessment has been done so, limited institutional, technical and financial capacity and low research and development capacities, overfishing, wetland degradation, Dam construction, deforestation and expansion of agriculture, and Urbanization and industrialization [2,9,10,24]. These activities are affecting the Ethiopian fishery production directly or indirectly.
More or less, all water bodies in Ethiopia are under a serious problem. The cause of water body’s degradation and loss are multidimensional and complex, which leads to various unexpected costs to the society and environment, the problems usually receive less attention [25]. Therefore, management is needed to minimize factors and to improve the conditions of water bodies. According to FAO defined fisheries management as ‘‘integrated process of information gathering, analysis, planning, decision-making, allocation of resources, and formulation and enforcement of fishery regulations by which the fishery management authority controls the present and future fishing activities, to ensure the continued productivity of the living resources in’’, which implies to regulate the exploitation of the biomass to the level that the resource remains sustained [26]. In the other way, fishery management measures like prohibition of destructive gears such as poisonous and explosive gears of any type are fully in place; mesh regulation including both twine and mesh size, and dimensions of the net need to be standardized and adjusted to the needs and requirements of individual fish species; some area and seasonal closure have been implemented and reserve park area have been declared [27]. Area and seasonal closure refers to a protection of those parts of the lake where the target species are known to breed, whereas a reserve area is permanently closed for fishing. Fishing activities not recommended during breeding seasons.
The capacity building and education programs can be contributed to lakes policies, legislation and regulation, community empowerment, pollution control, initiatives related to climate change, invasive alien species control, threatened species conservation, and adaptive management of ecosystems in response to a changing environment [25]. An integrated watershed management approach of the lake and its surroundings should be developed, rather than focusing only on the water bodies itself. For instance, developing of constructed wetland or establishment of waste treatment plant around the water bodies restores the lakes water quality. Especially riverine fishery should be taken in consideration during the construction of dam for hydropower and irrigation purpose [9].
Illegal fishing activities (like use of monofilaments, Seeds of Birbira tree (Millettia ferruginea) with Malathion and fencing must be totally prohibited. Public awareness creation towards illegal fishing, environmental degradation, and waste problems should be induced, as acceptance of the problem and behavioral changes by householders [9]. Additionally, the value and role of indigenous and traditional people in knowledge should not be left out when setting up awareness, advocacy, and capacity building [28]. Management strategies should comprise both biophysical and socioeconomic aspects with emphasis on issues like adoption of watershed/ecosystem approaches at policy level, integration of income generation in conservation activities, sharing of responsibilities/benefits among local stakeholders, institutional strengthening for environmentally and socioeconomically sustainable development of lakes [9].
Ethiopia has over 200 fish species in freshwater bodies, which belong to 75 genera, 31 families, and 12 orders. From the total number of fish species, 194 are native, 40 are endemic, and 6 are exotic species. The distribution of fish species and overall diversity within the drainage systems is extremely uneven. The highest fish species of two diversities in Ethiopia has been recorded from Baro basin, followed by Abay, Wabishebele, and Omo-Gibe basins but endemicity seems to be highest in Abay and Awashbasins. The actual fish production is still far below the estimated potential yield due to different constraints including illegal fishing activities, lack of awareness of the community in fisheries management, overfishing, wetland degradation, Dam construction for hydropower and irrigation, deforestation, invasive species, lack of infrastructure and technologies. The main fishery management strategies in Ethiopia including Capacity building and education programs can be contributed to lakes policies, legislation and regulation, community empowerment, pollution control, invasive alien species control, threatened species conservation, integrated watershed management plan, prohibition of destructive gears, area and seasonal closure and public awareness creation.
Public awareness is needed towards environmental degradation, illegal fishing activities, proper utilization of aquatic resources, and fishery management. Capacity building is needed in various aspects of aquatic policy, legislation and regulation, community empowerment, pollution control, and encouraged environmental conservation. Gear restriction such as mesh size regulation, catch limits, closed season, or area is the most common regulatory measure needed to maximize fish production. Improving the educational level of households living around the water bodies and facilitating diversified income generating opportunities for the households living around the water bodies is also necessary in dealing with the condition. The Government of Ethiopia needs to prepare and implement an integrated water resources and fisheries management plan in the drainage basin of Ethiopia with full participation of all relevant stakeholders including the riparian community to sustain the water system in the basin. Improve fishery policies and strategies for enhancing private sector investments in fishery development.
The authors declare that there are no conflicts of interest.
There is no funding source available.
Citation: Desalegn T, Shitaw T (2021) Fishery Resources, Conservation Challenges and Management Strategies in Ethiopia. Fish Aquac J. 12:273.
Received: 09-Feb-2021 Accepted: 23-Feb-2021 Published: 02-Mar-2021 , DOI: 10.35248/2150-3508.21.12.273
Copyright: © 2021 Desalegn T, et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.