In Africa, there has been an awakening or rather a revival of interest during recent years to introduce exotics and non-endemics, particularly for the development of aquaculture from a subsistence level activity to a commercial-scale operation. This is because all the developing countries are in need of increasing their food production in order to increase the protein-calorie intake of their people (FAO, 1975). It seems, therefore, that more introductions will take place in the near future.
There is no reason why exotics and non-endemics should not be imported provided that when an introduction is proposed, the necessity for the introduction and its merits is clearly established and no decision to stock must be taken until all aspects of the case, including the history of previous introductions of similar nature elsewhere in the world, have been taken into consideration (Hora and Pillay, 1962; Jackson, 1960). Once an introduction is recommended, controlled experiments must be conducted to assess their influence on the local fauna (Hora and Pillay, 1962). This means that whenever possible, trial introduction sites should be confined to closed water systems of manageable size that will permit close surveillance of predator establishment or otherwise and efficiency. This precaution is also important to facilitate early eradication of the species introduced should it show signs of becoming a pest (James and Fouler, 1970). This is because once it has escaped into the local streams, it tends eventually to spread over a wide area and unless the species cannot withstand competition with the local fish fauna and is soon eliminated, a fish introduction cannot be undone or repaired as with a chemical accident. It is a permanent thing and its impact on the local fish goes on throughout time (WHO, 1973). Under these circumstances a decision to introduce an exotic or non-endemic fish should not be taken lightly.
In this connexion, I would like to point out to the members of this Symposium the necessity of establishing an Advisory Committee for fish introductions into Africa so that any African country interested in introducing any species should seek the help and opinion of this Committee, whether or not there exist within the area any fish species of high biological or aesthetic interest, or which may be rare or endangered, that may be threatened by such introductions.
With respect to the species which have already been introduced into Africa, it is recommended that:
handicaps in trout transplantation to higher altitudes should find a solution
carp culture should be encouraged but its transplantation into natural waters should be prevented
great care should be exercised in the introduction of Gambusia affinis into new ecosystems; endemic T. nilotica should be used as a larvivore
introduction and cultivation of shellfishes in Africa should be encouraged
the production of 100% males of Tilapia spp. through hybridization with non-endemics should be popularized
pond culture of Clarias lazera, Heterotis niloticus should be encouraged and a solution for the difficulties to obtain natural spawning in ponds of the latter should be found
unsuccessful introductions should be eradicated.
My grateful thanks due to Dr. Z.H. Shehadeh, Technical Secretary, CIFA Symposium on Aquaculture in Africa for inviting me to write on this subject and to Dr. Y.B. Abu Gideiri, Head of Zoology Department, University of Khartoum, for reading the manuscript and useful suggestions.
For all the information obtained on the subject, through personal communication, I am indebted to the following scientists:
Ardill, U.D. (Mauritius), Atir, D.D. (Nigeria), Agr. Senior Fisheries Officer (The Gambia), Bard, J. (Centre Technique Forestier Tropical), Bishai, H.M. (Egypt), Cuerden, C. (FAO Fisheries Branch Library), Elloit, O.O. (Nigeria), Gay, W. (Zambia), Hogendoorn, H. (Cameroon), Ibrahim, K.H. (Tanzania), Kanyike, E.S. (Uganda), Lessent, P. (Centre Technique Forestier Tropical), Meskal, F.H. (Ethiopia), Ngaram A. (Tchad), Nasfi, H.F. (Tunisia), Vieyra, A.R. (Ivory Coast), and Vincke, M. (Central African Republic).
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APPENDIX I
Principal exotic and non-endemic cultivable
species deliberately introduced into Africa
Family | Species | Common names | ||
French | English | |||
Exotic Fishes | Salmonidae | Hucho hucho Berg (Salmo hucho L.) | Huchon | Huchen |
Oncorhynchus tschswytsche (Welbaum) | Saumon chinook | Chinook salmon | ||
Salmo gairdneri Richardson | Truite arc-en-ciel | Rainbow trout | ||
Salmo irideus Gibbon | Truite arc-en-ciel | Steelhead trout | ||
Salmo trutta L. | Truite de mer | Sea trout | ||
Salmo trutta macrostigma (Dumeril) | ||||
Salmo letnica | ||||
Salvelinus fontinalis (Mitchill) | Saumon de fontaine | Brook trout | ||
Salvelinus namaycush (Walbaum) | Omble américain | Lake trout | ||
Esocidae | Esox lucius L. | Brochet | Northern pike | |
Esox masquinongy Mitchill | Muskellunge | Muskellunge | ||
Centrarchidae | Eupomotis gibbosus (L.) | Perche soleil | Pumpkinseed | |
Lepomis macrochirus Rafinesque | Bluegill | Bluegill | ||
Lepomis microlophus (Gunther) | Redear sunfish | |||
Micropterus dolomieu (Lacépède) | Black-bass à petite bouche | Smallmouth bass | ||
Micropterus punctulatus Rafinesque | Black-bass tacheté | Spotted bass | ||
Micropterus salmoides (Lacépède) | Black-bass à grande bouche | Largemouth bass | ||
Morone (= Roccus) saxatilis | Striped bass | |||
Pomoxis annularis Rafinesque | White crappie | |||
Pomoxis nigromaculatus (Lesueur) | Black crappie | |||
Cyprinidae | Barbus holubi | |||
Carassius auratus (L.) | Carassin doré | Goldfish | ||
Catla catla (Hamilton Buchanan) | Catla | Catla | ||
Ctenopharyngodon idella Valenciennes | Carpe herbivore | Grass carp | ||
Cyprinus carpio L. | Carpe | Carp | ||
Hypophthalmichthys molitrix (Val.) | Carpe argentée | Silver carp | ||
Labeo rohita (Hamilton Buchanan) | Rohu | Rohu | ||
Scardinius erythropthalmus (L.) | Rotengle | Rudd | ||
Tinca tinca (L.) | Tanche | Tench | ||
Percidae | Perca fluviatilis (L.) | Perche | Perch | |
Sander lucioperca (L.) | Sandre | Pike-perch | ||
Gambusia affinis halbrooki | Gambusia | Gambusia | ||
Anabantidae | Osphronemus goramy (Lacépède) | Gourami | Gourami | |
Osphronemus olfax | ||||
Non-endemic Fishes | Osteoclossidae | Heterotis niloticus (Ehrenbaum) | Heterotis | Heterotis |
Clariidae | Clarias lazera | Catfish | ||
Centropomidae | Lates niloticus (L.) | Capitaine | Nile perch | |
Cichlidae | Astatoreochromis alluaudi (Pellegrin) | |||
Etroplus suratensis (Bloch) | Pearl spot | |||
Tilapia andersonii (Castelnau) | Tilapia(No. 106–121) | Tilapia(No. 106–121) | ||
Tilapia aurea (Steindachner) | Tilapia | Tilapia | ||
Tilapia hornorum Trewavas | ||||
Tilapia macrochir Boulenger | ||||
Tilapia melanopleura Dumeril | ||||
Tilapia mossambica (Peters) | ||||
Tilapia nigra (Gunther) | ||||
Tilapia nilotica (L.) | ||||
Tilapia rendalli (Boulenger) | ||||
Tilapia shirana Boulenger | ||||
Tilapia zillii (Gervais) | ||||
Serranochromis robostus | ||||
Exotic Shellfishes (Crustacea, mollusca) | Astacidae | Procambarus clarkii | Louisiana red crayfish | |
Palaemonidae | Macrobrachium rosenbergii (de Man) | Giant freshwater prawn | ||
Ostreidae | Crassostrea gigas | Pacific oyster (Japanese oyster) | ||
Crassostrea virginica | American oyster (Eastern oyster) | |||
Ostrea edulis | Flat oyster (Native European oyster) |
APPENDIX II
Cultivable species deliberately
introduced by the African countries
Family | Species | Country Introduce | Source | Date | Remarks |
Salmonidae | Hucho hucho Berg (Salmo hucho L.) | Morocco | - | - | Experimental, no success, cold-water fish |
Oncorynchus tschwytscha | Malagasy Republic | U.S.A. | 1955 | Unsuccessful | |
Salmo irideus | Malagasy Republic | France | 1922 | - | |
Salmo gairdneri | Lesotho | - | - | - | |
Kenya | Rep. South Africa | 1923 | For sport fishing | ||
Tunisia | France, Fed.Rep.Gry. | 1965 | - | ||
Uganda | - | - | Stocking natural waters (mountain streams) | ||
Sudan | Kenya | 1947 | Established in Nagishot and Kitiri | ||
Ethiopia | Kenya | 1967 | Rivers Danka and Web. | ||
Swaziland | - | 1904 | - | ||
Rep. South Africa | - | 1923 | - | ||
Morocco | U.S.A. and Switz. | 1971 | - | ||
Salmo trutta | Ethiopia | Kenya | 1967 | Rivers Danka and Web. | |
Swaziland | Rep. South Africa | 1914 | - | ||
Salmo trutta macrostigma | Morocco | - | - | For sport fishing | |
Salmo letnica | Morocco | - | - | For sport fishing | |
Salvelinus sp. | Morocco | - | - | For sport fishing | |
Esocidae | Esox lucius | Tunisia | France | 1966 | - |
Malagasy Republic | France | 1951–1958 | For sport fishing | ||
Morocco | Switz., France, Poland | 1934 | - | ||
Esox mosquinongy | Morocco | Switzerland | - | - | |
Centrarchidae | Eupomotis gibbosus | Morocco | France | - | - |
Lepomis macrochirus | Swaziland | Unknown source | 1939 | - | |
Congo | - | - | For blackbass feeding | ||
Morocco | - | - | Introduced by private enterprise | ||
Zambia | - | - | For blackbass feeding | ||
Malagasy Republic | Mauritius | 1954 | |||
Lepomis microlophus | Mauritius | - | 1944 | - | |
Morocco | U.S.A. | - | Introduced by private enterprise | ||
Micropterus dolomieu | Swaziland | Rep. South Africa | 1935 | - | |
Micropetrus punctulatus | Swaziland | Rep. South Africa | 1940 | - | |
Micropetrus salmoides | Kenya | - | 1928 | For sport fishing; Tilapia control | |
Egypt | - | 1949 | Unsuccessful | ||
Tunisia | Morocco | 1965 | - | ||
Malagasy Republic | - | 1861 | For Tilapia control | ||
Uganda | Kenya | - | - | ||
Swaziland | Rep. South Africa | 1933 | For sport fishing | ||
Mauritius | - | 1949 | - | ||
Kenya | - | - | For sport fishing | ||
Morocco | France | - | For sport fishing | ||
Cameroon | - | - | Did not spawn in ponds | ||
Congo | - | - | For Tilapia control | ||
Mozambique | - | - | For Tilapia control | ||
Rhodesia | - | - | Together with Lepomis | ||
Morone saxatilis | Rep. South Africa | U.S.A. | 1971 | For sport fishing | |
Pomoxis annularis | Morocco | - | - | - | |
Pomoxis nigromaculatus | Morocco | - | - | - | |
Cyprinidae | Barbus holubi | Rhodesia | Rep. South Africa | 1964 | Established in Lake Kyle, in 1965 |
Carassius auratus | Malagasy Republic | - | - | - | |
Mauritius | - | 1953 | - | ||
Catla catla | Mauritius | India | 1960,1973 | - | |
C. idella | Egypt | Hong Kong | 1968 | Weed control in canals | |
Kenya | Japan | - | - | ||
Uganda | Hong Kong | 1965 | Weed control in dams | ||
Sudan | India | 1975 | Experimental | ||
Ethiopia | Japan | 1975 | Weed control in Fincha Dam | ||
Rep. South Africa | Malagasy | 1967 | Experimental | ||
Cyprinus carpio | Central African Rep. | Israel, Cameroon | 1966,1975 | First stock disappeared from ponds | |
Lesotho | Rep. South Africa | 1969 | Experimental | ||
Kenya | Japan, Israel | - | Experimental | ||
Egypt | Indonesia, France, Syria | 1934 1949, 1970 | For pond culture and rice fields | ||
Tunisia | France | 1965 | - | ||
Malagasy Republic | France | 1914,1959 | For pond culture and rice fields | ||
Uganda | Israel | 1957 | For pond culture | ||
Ethiopia | ? | 1936,1940 | In Akoki Dam | ||
Sudan | India | 1975 | Experimental | ||
Ghana | Nigeria | 1962 | Unsuccessful | ||
Nigeria | Austria, Israel | 1954,1964 | For pond culture | ||
Rwanda | - | - | - | ||
Cameroon | U.S.A., Israel | 1970 | For rural fish culture | ||
Rep. South Africa | Bavaria | 1859 | - | ||
Togo | Israel, Nigeria | 1965,1971 | |||
Morocco | France | - | In rice fields | ||
H. molitrix | Egypt | Japan | 1962 | Experimental | |
Ethiopia | Japan | 1975 | For stocking Fincha Dam | ||
Labeo rohita | Mauritius | India | 1961 | - | |
S. erythropthalmus | Tunisia | France | 1965 | - | |
Morocco | France | - | In rice fields | ||
Malagasy Republic | France | 1951 | |||
Tinca tinca | Tunisia | Morocco | 1965 | - | |
Malagasy Republic | France | 1926–1951 | In rice fields | ||
Morocco | France | - | In rice fields | ||
Percidae | Perca fluviatilis | Morocco | Switzerland | - | - |
Lucioperca lucioperca | Morocco | Fed. Rep. Germany | - | - | |
Gambusia affinis | Central Afr. Republic | Brazzaville | 1958 | Disappeared from ponds after few months | |
Sudan | Italy | 1929 | Malaria control | ||
Ghana | - | - | - | ||
Malagasy Republic | - | - | - | ||
Ivory Coast | - | - | - | ||
Egypt | - | - | - | ||
Anabantidae | Osphronemus goramy | Uganda | - | 1963 | - |
Osphronemus olfax | Mauritius | - | 1761, 1944 | - | |
Malagasy Republic | Mauritius | 1857 | |||
Osteoglossidae | Heterotis niloticus | Central Afr. Republic | Cameroon | 1956 | For pond culture |
Ivory Coast | Cameroon | 1959 | - | ||
Togo | - | - | - | ||
Gabon | - | - | - | ||
Cameroon | - | - | - | ||
Dahomey | (Cameroon - | - | - | ||
Malagasy Republic | (Central Africa Rep. | 1963 | Experimental | ||
Clariidae | Clarias lazera | Cameroon | Central Afr. Republic | 1972 | For pond culture and control of Tilapia |
Centropomidae | Lates niloticus | Lake Kioga | - | - | To fill niches |
Cichlidae | Astatoreochromis alluaudi | Central Afr. Republic | Cameroon | 1969 | For snail control |
Etropolus sp. | Mauritius | - | - | - | |
Tilapia andersonii | Tanzania | Zambia | 1968 | Hybridization with T. zillii | |
T. aurea | Uganda | Israel | 1962, 1966 | For hybridization | |
T. hornorum | Uganda | Zanzibar | - | For hybridization | |
Ivory Coast | Malaysia | 1967 | For hybridization | ||
T. macrochir | Central Afr. Republic | Zaire and Congo | 1953 | Abandoned in fish culture | |
Malagasy Republic | Brazzaville | 1951, 1955 | |||
Ivory Coast | Cameroon | 1958 | For hybridization | ||
Mauritius | - | 1955 | - | ||
Ghana | Kenya | 1962 | - | ||
T. melanopleura | Sudan | Brazzaville | 1953 | For weed control; eliminated | |
Malagasy Republic | Brazzaville | 1951 | |||
Uganda | Kenya | - | - | ||
Mauritius | - | 1956 | - | ||
T. mossambica | Egypt | Thailand | 1954 | For pond culture; abandoned | |
Malagasy Republic | Mozambique | 1956 | |||
Tunisia | Congo | 1966 | - | ||
Uganda | Zanzibar | 1962–1966 | For hybridization | ||
T. nigra | Kenya | Athi River | 1925–1927 | Stocking Lake Naivasha | |
Malagasy Republic | Kenya | 1950 | - | ||
Uganda | Kenya | 1962–1966 | - | ||
T. nilotica | Central Afr. Republic | Brazzaville | 1963 | - | |
Tunisia | France, Fed.Rp.Gry. | 1966 | - | ||
Ivory Coast | Black Volta | 1957 | - | ||
Mauritius | - | 1957 | - | ||
T. rendalli | Central Afr. Republic | Zaire and Congo | 1953 | Abandoned in fish culture | |
T. shirana | Malagasy Rep. | Malawi | 1969 | Experimental culture | |
T. zillii | Ivory Coast | Congo | - | For hybridization | |
Ethiopia | Uganda | 1974 | For hybridization | ||
Malagasy Republic | Kenya | 1955 | |||
Mauritius | - | 1957 | - | ||
Kenya | Lake Albert | - | - | ||
Serranochromis robustus | Rep. South Africa | Upper Zambesi | - | - | |
Astacidae | P. clarkii | Uganda | - | - | - |
Palaehonidae | M. rosenbergii | Malawi | Thailand | 1973 | Experimental |
Ostreidae | C. gigas | Gambia | U.K. | 1975 | - |
Mauritius | U.S.A. | 1971 | - | ||
Seychelles | U.S.A. | 1973 | - | ||
C. virginica | Mauritius | U.S.A. | 1972 | - | |
O. edulis | Mauritius | U.S.A. | 1972 | - |
by
R. Lema, B. Giadom and K.H. Ibrahim,
Freshwater Fisheries Institute, Nyegezi,
P.B. 1213, Mwanza, Tanzania
Abstract
Aquaculture in Tanzania, mostly practised with a few species of tilapia, is faced with the common problem of excessive breeding leading to overcrowding and stunted growth. The report that Tilapia andersonii (Castelnau) matured in ponds in Zambia in 12–15 months time and that the species bred only once a year gave the idea that this species would probably fare better in Tanzania. Hence in 1968 an experimental consignment was introduced into Tanzania from Zambia and experiments carried out at the experimental fish farm at Malya. Results indicated that T. andersonii adapted to local conditions, matured and bred in three to five months time and in growth, survival and production etc. behaved in no way different from other species of tilapia available locally.
Resumé
En Tanzanie, l'aquiculture, qui consiste essentiellement en l'élevage de quelques espèces de tilapia, se heurte au problème courant d'une prolificité excessive conduisant au surpeuplement et au rabourgissement. Comme il a été rendu compte que, dans les étangs de Zambie, Tilapia andersonii (Castelnau) parvient à maturité sexuelle au bout de 12 à 15 mois et ne se reproduit qu'une fois par an, on a pensé qu'il serait probablement plus aisé d'engraisser cette espèce en Tanzanie. Aussi, en 1968, une livraison expérimentale en provenance de la Zambie a-t-elle été introduite en Tanzanie et des expériences ont elles été effectuées à la station expérimentale de pisciculture de Malya. Les résultats ont montré qu'après adaptation aux conditions locales, T. andersonii parvient à maturité et se reproduit au bout de 3 à 5 mois et que sa croissance, sa survie et sa productivité ne diffèrent en rien de celles des autres espèces de tilapia trouvées sur place.
Subsequent to the initiation of systematic pond culture in the forties with several species of tilapia, aquaculture has been faced with several problems. After an initial explosive growth of aquaculture in Africa, further progress and development came to a standstill or suffered a serious setback (Bard, 1962; Lemasson and Bard, 1964; Meschkat, 1967). Early maturation and repeated breeding of tilapia under tropical pond conditions, leading to overcrowding in ponds, are considered to be the major factors that led to the present impass in fish culture development. However, various techniques such as mono-sex culture, use of predators in tilapia ponds, use of sterile or mono-sex hybrids, use of better and fast-growing species, etc., have been suggested by several workers and investigations carried out on these lines.
The present status of aquaculture in Tanzania (Gould, 1951; Ibrahim and Lema, 1974a, 1974b; Ibrahim et al., 1974; Ibrahim, 1975; Matthes, 1974) is in no way different from the conditions mentioned above. Among the species cultivated in ponds in Tanzania, Tilapia esculenta, T. rendalli, T. zillii, T. nilotica, T. pangani, T. rukwensis, etc., respond in a similar manner regarding growth maturation and breeding. Hence it was felt that a fast-growing species would be more suitable for culture. At this time the report that T. andersonii matured in ponds in Zambia in 12–15 months time and that the species bred only once in a year (Maar et al., 1966; Meecham, 1962; Meschkat, 1967) gave the idea that probably this species could fare better in Tanzania. Thus an experimental consignment of T. andersonii was introduced into Tanzania from Zambia in 1968 (Anon., 1971; Ibrahim and Lema, 1974b).
The main purpose of the experiments was to (1) find out the utility of T. andersonii for pond culture in Tanzania and (2) determine whether this species behaved differently from other local tilapias, particularly regarding maturation and breeding.
In July 1968 an air consignment of 100 fingerlings of T. andersonii (average length of 100 mm and 56.6 g weight) under oxygen packing was brought to Mwanza and stocked in a specially prepared pond of 0.08 hectar area at the small experimental fish farm at Malya, about 125 km from Mwanza (Fig. 1). The fish were fed daily on rice sweepings obtained locally, at a rate approximately equal to the weight of fish stocked. By November 1968, or in about four months time, specimens with an average length of 189 mm and 188.8 g weight bred, and fry were available.
A total of 500 fry of T. andersonii produced locally from the first brood and of an average weight of 14 g were stocked in a prepared pond of 0.08 hectar area on 14 March 1969 to study growth and breeding. Feeding was as before with rice sweepings. The fish were sampled in 15 to 20 days and growth recorded. At the end of 142 days the pond was harvested by repeated netting followed by draining of the pond. A similar experiment was conducted with another set of T. andersonii fry of average weight 8.15 g. In this case 500 fry were stocked on 23 June 1971 in another 0.08 hectar pond and observations made as in previous experiments.
In the first experiment T. andersonii attained a size of about 120 g in about two months time and 170 g in four months time. In 142 days T. andersonii started breeding as evidenced by the presence of eggs and larvae in the mouth of several females. When the experiment was terminated, the survival among the 500 stocked was 61 percent. The growth pattern is presented in Figs. 2 and 3.
In the experiment initiated on 23 June 1971, fry of 8.2 g average weight attained an average weight of 88 g in five months. However, very early breeding was recorded when the average weight of the fish was only about 47 g or about three months after stocking.
These preliminary experiments indicate that the original stock imported, as well as the progeny produced locally, matured and bred in less than five months time under local conditions. Thus T. andersonii, under local conditions in Tanzania behaved similarly to local species with regard to maturation and breeding. Differences in temperature and other ecological factors between Zambia and Tanzania could be responsible for this type of differential behaviour.
However, T. andersonii, a reportedly plankton feeder, could adapt to local conditions in Tanzanian waters and could be a welcome addition to the locally available cultivable species.
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Fig. 1. A view of the experimental fish farm at Malya where Tilapia andersonii (Cast.) was introduced.
Fig. 2. Growth rate of T. andersonii in experimental fish ponds at Malya.
Fig. 3. Growth rate of T. andersonii at the experimental fish farm at Malya.