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Growing poverty and population in Africa
increases the pressure on governments to maximize
food production as rapidly and as cheaply as
possible. Urgency often results in a failure to
carefully review costs and benefits. Policy-makers
trying to feed hungry people and investors seeking
quick returns are strongly compelled by the
perceived magic bullet of importing an exotic
species that has proven its worth in other
countries or regions.
However, the track record of aquaculture-related
introductions in Africa (see Table 1)
shows that bringing in exotic species to get quick
results seldom produces the desired outcome. In
reviewing 212 international introductions into
Africa of freshwater fishes for aquaculture, only
33 (16%) were found to have resulted in the
establishment of an industry with output of more
than 10 mt per year in 1997. Of these, 10 (30%)
were of common carp (Cyprinus carpio) from
Asia and Europe and 7 (21%) were of Nile tilapia
(Oreochromis niloticus) from other African
countries. Typical is the case of Zambia where 39
introductions resulted in sustained aquaculture of
only Nile tilapia and common carp. Production of
these two species in 1997 was only 133 and 275mt,
respectively, compared to 2 680 and 1 010 mt for
the indigenous Oreochromis andersonii and
Tilapia rendalli, respectively (see Table
2).
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Table 1. Effects of some
characteristic aquaculture-related
introductions in Africa
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Aquaculture
Introduction
|
Environmental
Impact
|
Tonnes Cultured1
|
|
Oreochromis niloticus to
Kenya
|
Displaced endemic O. esculentus
in Lake Victoria
|
124
|
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Tilapia. zillii to Uganda
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Displaced O. variabilis in Lake
Victoria
|
20
|
|
Osphronemus goramy to
Mauritius
|
Naturalized, minimal
|
0
|
|
Oreochromis macrochir and
Tilapia rendalli to Cameroon
|
Naturalized, unknown
|
0
|
|
Cyprinus carpio to Kenya
|
Displacement of local spp.
|
<0.5
|
|
C. carpio to Zambia
|
Not established
|
275
|
|
C. carpio to Malawi
|
Not established
|
<10
|
|
C. carpio to Zimbabwe
|
Naturalized
|
0
|
|
O. niloticus to Zimbabwe
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Introgression and reduced catches of
indigenous tilapias
|
133
|
|
Clarias gariepinus to
Cameroon
|
Naturalized
|
<0.5
|
|
Carassius auratus to
Madagascar
|
May have introduced parasites
|
0
|
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Chinese carps to Ethiopia
|
Reportedly naturalized
|
2
|
|
Ctenopharyngodon idella to
RSA
|
Introduced fish tapeworm
|
<0.5
|
|
C. carpio to Madagascar
|
Naturalized
|
6105
|
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C. carpio to RSA
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Reduced catches of local spp.;
introduced 7 exotic parasites
|
35
|
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Heterotis niloticus to
Côte d'Ivoire, Cameroon, CAR,
Gambia, Congo
|
Naturalized
|
2
|
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Oncorhynchus mykiss to
Morocco
|
Unknown
|
100
|
|
Salmo trutta to RSA
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Eradication of local spp.
|
0
|
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O. niloticus to Madagascar
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Genetic introgression and replacement
of local spp.
|
0.5
|
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1 As reported to FAO
(1999)
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In terms of weight produced, over 99 percent of
the total production of exotic species in Africa in
1997 was of common carp in only two countries,
Egypt (22 mt) and Madagascar (6 mt). Currently, the
common carp industry in Egypt is in serious decline
due to reduction of government subsidies and
consumer preference for the indigenous Nile
tilapia. In total, exotic species account for 15
percent of African aquaculture output. In Asia, the
powerhouse of world aquaculture, 517 introductions
have resulted in a total contribution of 5 percent
to total output.
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Table 2. Production of
indigenous species in selected African
countries1
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Country
|
Species or Species
Group
|
1997 Production
(mt)
|
|
Côte d'Ivoire
|
Siluroids
|
192
|
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Egypt
|
Mugil cephalus
|
11 931
|
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Oreochromis niloticus
|
30 416
|
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Clariids
|
230
|
|
Ghana
|
Oreochromis niloticus
|
300
|
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Clarias gariepinus
|
100
|
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Kenya
|
Oreochromis niloticus
|
124
|
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Malawi
|
Mixed tilapias
|
>300
|
|
Nigeria
|
Characoids
|
3 480
|
|
Heteroitis niloticus
|
2 956
|
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Clariids
|
5 357
|
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Synodontids
|
550
|
|
Sudan
|
Oreochromis niloticus
|
1 000
|
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Tanzania
|
Oreochromis niloticus
|
250
|
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Tunisia
|
Mugil cephalus
|
485
|
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Zambia
|
Oreochromis andersonii
|
2 680
|
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Oreochromis macrochir
|
407
|
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Tilapia rendalli
|
1 010
|
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1As reported to FAO
(1999)
Only those industries with output of
>100 mt are listed
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The main reason why exotics have failed to
produce better growth of the aquaculture sector in
Africa is because the germplasm being cultivated is
only one, and not currently the most important,
constraint to development. Africa possesses
adequate aquatic biodiversity to sustain
aquaculture development. Asia, the world leader in
aquaculture, relies on exotics for only five
percent of total production and the number of
indigenous freshwater fish species in Asia and
Africa is approximately the same, 2 943 and 2 660,
respectively (Christine Casal, ICLARM,
Personal Communication, November 1999). Far more
important than lack of species are inadequate
inputs, shortage of seed, lack of the necessary
research, development and extension (R, D & E)
to backstop industrial growth and poor market
development. While inadequate inputs affect
indigenous and exotic species alike, indigenous
species may have an advantage in seed production,
R, D and E and markets.
Well over 90 percent of the African fish farming
sector are smallholders. To be viable and
self-sustaining, the smallholder sector needs
species that can be reproduced without complicated
and/or expensive interventions. Encouraging
dependence upon exotic species that require
hatchery facilities for propagation will only
exacerbate the fingerling supply problem.
Inadequate hatchery reserves of broodfish are a
major cause of inbreeding depression in cultured
stocks. For indigenous species, there are ready
reserves of broodstock that are already adapted to
local environmental and climatic conditions for
their reproduction.
New feeds, disease therapies, reproduction
techniques and sometimes even pond designs are
needed when species additions or changes are taking
place. The R & D process, through which new
management strategies are developed, is probably
the best way to produce both the needed technology
and the skilled scientists and extension personnel
to support aquaculture development. Exotic species
are normally introduced to only one research
facility at a time. In situations where high
quality human resources are in short supply, this
may limit the number of researchers studying the
domestication of a particular species to only one
or two. With indigenous species, any student,
scientist, would-be farmer or extension agent in
the country can get involved.
Many technology-driven development initiatives
introduce complete production systems (including
the culture species) more or less without regard to
markets. The common carp industry in Egypt is a
good example. Carp were introduced as an ideal fish
for culture in rice paddies. Millions of carp
fingerlings were produced in government hatcheries
and delivered at subsidised prices to rice farmers.
At give-away prices, these fish were a source of
cheap protein to the urban poor, but as government
subsidies declined and the price of carp rose to
cover costs, consumers with sufficient income
switched back to the indigenous tilapias while
poorer segments of the market simply didn't buy
fish. Carp production in Egyptian rice fields
collapsed from a reported 21 000 tonnes in 1996, to
less than 7 000 tonnes in 1997.
For whatever reasons, the track record shows
that indigenous African species are more likely to
contribute to local economic growth and put food
into African markets faster than exotics.
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