International Journal of Global Science Research
Vol. 6, Issue. 1, April 2019, pp. 909-915
Available Online at www.ijgsr.com
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ISSN: 2348-8344 (Online)
DOI: 10.26540/ijgsr.v6.i1.2019.118
Review
On the impact of Tilapia (Oreochromis mossambicus Peters, 1852) on the
Icthyodiversity: A Review
Yati Sood, Prahlad Dube, Jyoti Sharma and Arjumand Quershi*
Department of Zoology, Government College, Kota, Rajasthan, India.
*Government College, Jhalawar, Rajasthan, India.
Email: dube.prahlad@gmail.com
Received: 05/03/2019
Revised: 12/03/2019
Accepted: 29/03/2019
Abstract:
Tilapia
(Oreochromis
mossambicus) is African mouth-brooder
cichlid fish. It is native to the eastward
flowing rivers of central and southern
Africa. Morphological features are quite
distinctive such as laterally compressed
body, approx 35cm in length and up to
1.13 kg in weight. It are omnivorous. In
India it was brought from Sri Lanka for the
first time.It’s invasion is problematic for
native diversity in many countries. It is
listed in Global Invasive Species Database
(2006). It is creating threat to local fish
fauna in India and other countries.
Therefore, it is very important to
understand the impact of it's presence in
Indian waters. Rajasthan is known for his
great Thar desert but south eastern part is
blessed with many perennial and emprical
rivers and lentic water bodies. Very less
work is carried out regarding impact of
tilapia on biodiversity of south eastern part
of Rajasthan. Present paper tries to review
the available literature on this area of study
which would be a great help to conserve
the native fish diversity.
Key words: fish diversity, tilapia, invasive
species, morphological features.
INTRODUCTION:
Tilapia is the common name for nearly a
hundred species of cichlid fish from the
tilapiine cichlid tribe. Tilapia are mainly
freshwater fish inhabiting shallow streams,
ponds, rivers and lakes and less commonly
found
living in
brackish
water.
Historically, they have been of major
importance in artisan fishing in Africa and
the Middle East, and they are of increasing
importance in aquaculture and aquaponics.
Tilapia can become problematic invasive
species in new warm-water habitats such
as Australia, whether deliberately or
accidentally introduced, but generally not
in temperate climates due to their inability
to survive in cold water.
The native Mozambique tilapia is laterally
compressed, and has a deep body with
long dorsal fins, the front part of which has
spines. Native coloration is a dull greenish
or yellowish, and there may be weak
banding. Adults reach approximately 35
centimetres (14 in) in length and up to 1.13
kilograms (2.5 lb). Size and coloration
may vary in captive and naturalized
populations due to environmental and
breeding pressures. It lives for up to 11
years.
Under auspices of Environment & Social Welfare Society, India
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Mozambique tilapia are omnivorous. They
can consume detrital material, diatoms,
invertebrates, small fry and vegetation
ranging from macro-algae to rooted plants.
This broad diet helps the species thrive in
diverse locations
The African mouth-brooder cichlid, the
Mozambique
tilapia,
Oreochromis
mossambicus Peters 1852, is native to the
eastward flowing rivers of central and
southern Africa (Philippart and Ruwet,
1982; Trewavas, 1982). Due to their
perceived utility as an aquaculture species,
Oreochromis mossambicus are now widely
distributed around the world (Arthington et
al., 1984; Philippart and Ruwet, 1982).
However, Oreochromis mossambicus have
now not liked as a preferred aquaculture
species because of their propensity to
‘stunt’ and their general poor quality due
to the small size of founder stocks (Pullin,
1988). Invasive populations are now
causing environmental and ecological
problems in many countries (Canonico et
al., 2005) and as such, Oreochromis
mossambicus is listed in the Global
Invasive Species Database (2006) as being
in the top 100 invasive alien species on the
planet.
The species has been described as a
‘model invader’ due to a number of key
biological
characteristics
including
tolerance to wide ranging ecological
conditions, generalist dietary requirements,
rapid reproduction with maternal care, and
the ability to successfully compete with
native fish through aggressive behavior
(Pe´rez et al., 2006b). Therefore, given
suitable
environmental
conditions,
Oreochromis mossambicus have become
successfully established in almost every
region in which they have been cultured or
imported
(Costa-Pierce,
2003;
Cucherousset and Olden, 2011; Diana,
2009; Strecker et al., 2011). Official
records
show
that
Oreochromis
mossambicus was first introduced to India
from Sri Lanka in 1952 and thereafter
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DOI: 10.26540/ijgsr.v6.i1.2019.118
stocked in several reservoirs of southern
India for production enhancement
(Sugunan, 1995). Tilapia now forms a part
of fish fauna in the Godavari, Krishna,
Cauvery, Yamuna and Ganga Rivers
(Lakra et al., 2008).
In earlier studies, tilapia attracted the
attention of scientific communities due to
its mouth brooding behaviour (Perez et al.,
2006; Russell et al., 2012). Tilapia has
remained an objective of astonishment to
ethnologists for years but its present
behaviour, that is, prolific feeder and
prolific breeder changed the scenario.
Tilapia is now known for its invasion to
the non-native water bodies and
destruction of their flora and fauna.
REVIEW:
The Icthyodiversity and impact of invasive
species on it has been a popular subject
among the scientist all over the globe. The
most widely dispersed tilapia species the
Mozambique
tilapia
(Oreochromis
mossambique) which was once known as
the Java tilapia since most introduction of
this fish originated from west Jawa,
Indonesia, its first established local outside
Africa (Hickling 1960). Due to the small
size of founder stocks, by the mid -1970
the Mozambique tilapia deteriorated in
many recipient environment and small
sized, poor quality fish lost consumer
acceptance [Pullin1988].
Allonson et al., (1971) suggested that
Tilapia mossambicus to estuaries at the
southern end of its distribution at the
sourthen Africa related to the maintenance
of near normal Na and Cl ion
concentration at low temperature during
winter water.
Moriarty (1973) reported that the cells of
blue green algae are lysed by high
concentration of acid (pH 1.9 – 1.4) in the
stomach of Tilapia nilotic. After laysis,
cell contain are digested in the intestine.
Acid secretion follows diuranal cycle
Under auspices of Environment & Social Welfare Society, India
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related to feeding and thus there is a cycle
from zero to maximum digestion each day.
Kutty and Sukumaran (1975) reported that
Tilapia mossambicus to
C in fresh
water and forced to swim at current speeds
36, 66 and 82 cm/s in Blazka’s activity
apparatus failed to swim at 39.7, 38.4 and
respectively when temperature
become increase lower critical temperature
of swimming failure at the same three of
ambient water was gradually increased
from
the
acclimation
temperature
swimming speeds were 17.4, 10.8 and
C the pattern of swimming failure at
the critical temperature was similar to that
at critical ambient
concentration.
Bruton et al., (1975) reported that Tilapia
mossambicus inhabits the littoral and sublittoral in the warm and transition period
(Aug. Apri) but move into deep water in
the cool season (May- July). Exposed and
sheltered areas are utilized for different
purpose by adult fishes, the former for
nesting, and latter for feeding and mouth
brooding.
Hwang (1987) reported that the
development of leaky junctions and
interdigitations in branchial chloride cells
appear to correlate to seawater adaptation
in Oreochromis mossambicus. These
change of seawater-adapted chloride cells
seem to be associated with the increase of
ion permeability in the gills of teleosts
adapted to seawater rather than those
adapted to fresh water.
Pullin and Cupili (1987) reported the
tilapia are cultured throughout the tropics
and subtropics for genetics improvement.
They also reported that largest tilapia
culture industries are in Asia. The
emphasis is on the most popular cultured
species, Oreochromis niloticus
De Silva and Sirisena (1988) reported that
Oreochromis mossambicus formed nest
build in five manmade lake Sri Lanka. The
nest always found generally located in or
near cover in shallow water. The nests
ranged from 11 to 110 cm in diameter, two
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DOI: 10.26540/ijgsr.v6.i1.2019.118
size groups of nest recognizable small,
with diameter 10-50 cm and large with
diameter >50 cm. At any nesting site only
one size group of nest was found.
Amarasinghe and de Silva (1992) have
reported that the performance of
Oreochromis mossambicus in Kaudulla
and Minneriya reservoirs was better than is
other various geographical area. This may
be due to very favorable environment for
Oreochromis mossambicus in Sri Lanka
reservoirs which provide variety of
nutrition food source.
Yada et al., (1994) observed that the
changes in GH (growth hormone) which
occurred when tilapia were moved
between fresh water and sea water are
compatible with idea proposed by other for
salmonids that GH may have important
role for sea water.
Oliveira and Almada (1995) reported that
sexual dimorphism in growth of
conventional morphometric character was
investigated in juvenile and young adult
(size range 31 to 91 mm) of Oreochromis
mossambicus. A closely associated set of
traits was identified that shows sexually
dimorphic growth which was positively
allometric in the male. These traits
correspond to two different morphological
complexes. Jaw structure and anal /dorsal
fins. The best sex discriminates among this
set of traits were premaxilla width and fin
height and snout. These finding may be
explained in term of intra and inter sexual
selection acting together and favouring
males with strong and large mouth and
high dorsal and anal fin, traits that are
important in agonistic display (jaw and
fins) fighting and nest digging (jaw).
Jayaprakas et al., (1996) observed that
carnitine induced lipid catabolism leading
to reduction in lipid content of cultured
fish, using lipid as energy source while
sparing protein for anabolic processes.
Significantly high GSI, sperm cell
concentration, motaility and percentage
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viability of the spermatozoa in carnitine
treated tilapia.
Vanzyl et al., (1997) reported that 24
Oreochromis mossambicus from the
Hardapdam, Namibia were introduced
during 1986, into salt pans at
Swakopmund on the Namibia coast. The
salt concentration of the salt pans is higher
than of sea water. The Oreochromis
mossambicus adapted well to the
condition,
breed
successfully
and
maintained a healthy population.
Nakano et al., (1998) suggested that
glucose is an important energy source for
osmoregulation during the acclimation to
hyperosmotic
environments
in
Oreochromis mossambicus.
Kumar (2000) reported that exotic species
and other anthropogenic activities the
exotics compete with the indigenous
species for food, habitat and may even
prey open them, introduced new parasites
and diseases. Oreochromis mossambicus
in India has been claimed as a success
story by expect. He found that tilapia now
dominates indigenous icthyofaunal in
many water bodies of India.
Canonica et al., (2005) has reported that
tilapia species are highly invasive and
exist under feral condition in every nation
in which they have been introduced. They
also found that tilapia damage to native
fish species and biodiversity.
Raghavan et al., (2007) reported that five
exotic found Chalakudy river in Kerala,
India. Oreochromis mossambicus was
ubiquitous in occurrence with large shoals
being encountered at all sampling sites
along the downstream upstream gradient
of the river.
Marjani et al., (2009) observed that 17alpha Methyl Testosterone [MT] receiving
treatment showed a significantly higher
male proportion than the control
experiment of Oreochromis mossambicus.
Dose rate of 75 mg/kg MT of feed resulted
in maximum male population [98.09%]
with 1.91% sterilized fish. The dose rate of
ISSN: 2348-8344 (Online)
DOI: 10.26540/ijgsr.v6.i1.2019.118
75 mg/kg MT gave the maximum gain in
body weight i.e., 11.8g which is 1.2 time
greater than the control.
Singh and Lakara (2011) have reported
that in India over 300 alien species are
present 291 invasive species, for example
Cyprinus carpio, Oreochromis niloticus,
Aristichthys nobilis, Pygocentrus natereri
and Pterygolichthys sps. They reduce the
availability of local species and establish
in natural water bodies becoming invasive
and consequently adversely affecting fish
biodiversity and aquatic ecosystem.
Adriana et al., (2011) reported that Nile
and mozambique tilapia harbour a number
of different species of Gyrodactylus, with
Gyrodactylus cichlidarum being the most
frequently
encountered
and
being
associated with mortalities of juvenile
Oreochromis niloticus niloticus.
Russell et al., (2012) reported that two
invasive tilapia species, Oreochromis
mossambicus and Tilapia mariae in fresh
water habitat in north-eastern Australia
was
investigated
Oreochromis
mossambicus length and age considerably
depending
on
habitat
male
and
Oreochromis mossambicus in a large
impoundment were considerably greater
than for those resident in small coastal
drain.
Singh (2014) reported that number of
invasion of fresh water exotic fishes have
taken place into India over the past decade
and
adversely
affected
the
fish
biodiversity. Many more change are
predictable to occur with the expected
climate invading near area and ecosystem.
The estimated annual average production
of alien species fit for human consumption
amount to around 18.2 to 34.5% of the
annual average production of marketable
fish culture in India. A significant negative
impact of the introduced species on native
icthyo fauna has been ascertiained as
regard to its ecological, biological
characteristic biodiversity and health.
Concidered a typical invasive alien
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species,
Oreochromis
mossambicus,
Oreochromis niloticus and Cyprinus
carpis heavily depressed the occurrence
and numbers of Indigenous population and
also contributed to the declined fishery of
native cyprinid fish in several natural
aquatic body of the country.
Ujjania et al., (2015)has reported that
during 1990-90 in Jaisamand IMC (37%),
Minor carp (59%) and Cat fishes (9%)
total production 287 metric ton but due to
invasion of tilapia where only IMC (11%),
Minor carp (3%), Cat fish (4%) and
Tilapia is dominating 82% out of total
production 119 Meteric ton.(2012-13)
Sakhare and Jetithor(2016) reported that
80
specimens
of
Oreochromis
mossambicus
collected from Borna
Reservoir of Maharashtra, India revealed
that
the food of juvenile mainly is
rotifer(35%),
copepode(30%),
chlorophyceae(20%),
bacillariophyceae(10%)
and
aquatic
insect(5%).
While
in
adult
gut
chlorophycaea
(40%),
bacillariophyceae(30%), rotifer(15%) and
aquatic insect(5%).Intense feeding was
noticed during
summer season and
juvenile was the active feeder.
Laxmappa (2016) reported that presence of
exotic fishspecies such as Oreochromis
niloticus, Oreochromis mossambicus,
Claris gariepinus etc have impacted the
population of indigenous species and
contributed towards the decline in the
fishery of native cyprinid fish species in
several natural aquatic bodies of
Telangana state.
Renjithkumar et al., (2016) reported that
the contribution of non native species to
the total fishery of Bharathapuzha River
was estimated to be 13.93%. Indian major
carp [Gibelion catla, Labeo rohita,
Cirrhinus mrigala] and Oreochromis
mossambicus were the non native species
represented in the exploited fishery.
Gibelion catla[3.98t], Labeo rohita [5.14t]
and Cirrhinus mrigala [3.14t] were the
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transplanted species which together
formed 11.43% in the total landing of the
river. The size range of Catla Rohu, Mrigal
in the catch were 240-720mm, 290560mm and 190-360mm respectively. The
exotic fish Oreochromis mossambicus
accounted for 25% of the fishery
CONCLUSION:
Concluding the above account we can state
that tilapia [Oreochromis mossambicus]
are popular exotic fish in fresh water
resources It’s invasion harm full for other
indigenous fishes species. Thus tilapia
[Oreochromis mossambicus] study is very
important for aquatic diversity.
REFERENCES:
Allanson B.R., Bok, A, and VanWyk, N.I.
(1971) The Influence of Exposure to Low
Temperature on Tilapia mossambica
Peters (Cichlidea). Journal of Fish
Biology, 3(2),181-185.
Amarasinghe U.S., and deSilva, S.S.
(1992)
Population
Dynamics
of
Oreochromis
mossambicus
and
Oreochromis niloticus (Cichlidae) in Two
Reservoirs in Sri Lanka. Asian Fisheries
Sciences 5(1),37-61
Arthington A.H., McKay, R.J., Russell,
D.J., and Milton, D.A. (1984) Occurrence
of the introduced cichlid Oreochromis
mossambicus (Peters) in Queensland.
Aust. J. Mar. Freshw. Res. 35(2), 267-272.
Bruton M.N., and Boltt R.E. (1975)
Aspect of the biology of Tilapia
mossambicus Peters (Pisces: Cichlidae) in
a natural fresh water (Lake Sibaya , South
Africa) Journal of Fish Biology 7(4), 423445.
Canonica G.C., Arthington A. McCrary
J.K. and Thieme M.L. (2005) The effect of
introduced tilapias on native biodiversity.
Under auspices of Environment & Social Welfare Society, India
Page 913
International Journal of Global Science Research
Vol. 6, Issue. 1, April 2019, pp. 909-915
Available Online at www.ijgsr.com
© Copyright 2014 | ijgsr.com | All Rights Reserved
ISSN: 2348-8344 (Online)
DOI: 10.26540/ijgsr.v6.i1.2019.118
fresh
Male Oreochromis mossambicus (Peters).
Fishery Technology, 33(2), 84-90
Costa-Pierce BA (2003) Rapid evolution
of
an
established
feral
tilapia
(Oreochromis spp.): the need to
incorporate
invasion
science
into
regulatory structures. Biol. Invasions 5:7184
Kutty M.N., and Sukumaran, N. (1975)
Influence
of
Upper
and
Lower
Temperature Extremes on the Swimming
Performance of Tilapia mossambica.
Journal Transaction of the American
Fishery Society 104(4), 755-761.
Cucherousset J, Olden JD (2011)
Ecological
impacts
of
non-native
freshwater fishes. Fisheries 36(5), 215–
230.
Kumar A.B., (2000). Exotic fishes and
fresh water fish diversity. Zoos’ Print
Journal, 15(11), 363-367
Aquatic conservation marine and
water ecosystem 15(5), 463-483.
de Silva S.S., and Sirisen H.K.G. (1988)
Observations on the nesting habits of
Oreochromis mossambicus (Peters) (Pices:
cichlidae) in SriLanka reservoirs. Journal
of Fish Biology, 33(5), 689-696.
Diana J. S. (2009) Aquaculture production
and biodiversity conservation. Bioscience
59(1), 27–38.
Garcia–Vasquez A., Hansen H. Christison
K.W. Bron J.E. and Shinn A.P. (2011).
Description of three new species of
Gyrodactylus von Nordmann, !832
(Monogenea) parasitising Oreochromis
niloticus niloticus [L.] and Oreochromis
mossambicus (Peters) (Cichlidae). Acta
Parasitological 56(1), 20-33
Hwang P.P. (1987) Tolerance and
ultrastructural response of
branchial
chloride cells to salinity changes in the
euryhaline
teleost
Oreochromis
mossambicus. Marine Biology 94(4):643649.
Laxmappa B., (2016). Exotic fish species
in aquaculture and aquatic Ecosystem in
Telangana State, India. Journal of Aquatic
Biology and Fisheries, 4:1-7
Lakra W.S., Singh, A.K., and Ayyappan,
S. (eds.) (2008). Fish Introductions in
India: Status, Potential and Challenges.
Narendra Publishers, New Delhi, India.
Marjani M., Jamili, S., Mostafwi, P.G.,
Ramin, M. and Mushiuchin, A. (2009).
Influence
of
17Alpha
Methyl
Testosterone on Masculinization and
Growth
in
Tilapia
(Oreochromis
mossambicus). Journal of Fisheries and
Aquatic Science 4(1), 71-74.
Moriarty D.J.W.,(1973). The physiology
of digestion of blue-green algae in the
Cichlid fish, Tilapia nilotica. Journal of
Zoology, 171(1), 25-39
Hickling C.F. (1960) The Malacca tilapia
hybrid. Fish culture research station,
Malacca. 57(1).
Nakano K., Tagawa, M. Takemura, and
A, Hirano, T. (1998). Temporal Change in
Liver
Carbohydrate
metabolism
Associated with Sea water transfer in
Oreochromis mossambicus. CBP Part B:
Biochemistry and Molecular Biology
119(4), 619-836
Jayaprakas V., Sambhu, Kumar, S. S.
(1996) Effect of Dietary L-carnitine on
Growth and Reproductive Performance of
Oliveira R.F., and Almada, V.C. (1995).
Sexual Dimorphism and Allometry of
External Morphology in Oreochromis
Under auspices of Environment & Social Welfare Society, India
Page 914
International Journal of Global Science Research
Vol. 6, Issue. 1, April 2019, pp. 909-915
Available Online at www.ijgsr.com
© Copyright 2014 | ijgsr.com | All Rights Reserved
mossambicus. Journal of Fish Biology
46(6), 1055-1064.
Philippart J.C. and Ruwet J.C. (1982).
Ecology and distribution of tilapias. In:
Pullin RSV, Lowe-McConnell RH (eds)
Biology and culture of tilapias.
International Center for Living Aquatic
Resource Management, Manila. pp. 15-59.
Pe´rez J.E., Nirchio, M., Alfonsi, C., and
Munoz C. (2006b). The biology of invasions: the genetic adaptation paradox. Biol.
Invasions 8, 1115-1121
Pullin R.S.V.,(1988). Tilapia genetic
resources for aquaculture. In: Pullin RSV
(ed) International Center for living aquatic
resources
management
conference
proceedings, Manilla, ICLARM. pp. 108.
Raghavan, R., Prasad, G. Anvar-Ali, P.H.
and Pereia, B. (2007). Exotic Fish in a
Global biodiversity hotspot observation
from river chalakndy, Part of western
ghats , Kerala, India. Biological invasions
(2008) 10(1), 37-40.
Renjithkumar C.R., Roshni, K. and
Madhusoodam, K.B. (2016). Composition
of Non Native Fishes in the Exploited
Fishery of Bharathapuzha River, Kerala,
India. Journal of Aquatic Biology and
Fisheries 4, 99-104.
Russell D.J., Thuesen, P.A. and Thomson,
F.E. (2012). Reproductive strategies of
two invasive tilapia species Oreochromis
mossambicus and Tilapia mariae in
northen Australia. Journal of Fish Biology
80(6), 2176-2197
Sakhare V.B., and Jetithor, S.G. (2016).
Food
and
feeding
behavior
of
Mozambique
tilapia
(Oreochromis
mossambicus
Peters)
from
Borna
Reservoir of Maharashtra, India . Journal
of Fisheries, 4(3), 431-439.
ISSN: 2348-8344 (Online)
DOI: 10.26540/ijgsr.v6.i1.2019.118
Singh A.K. and Lakra, W.S. (2011). Risk
and benefit assessment of alien species of
the aquaculture and aquarium trade into
India. Reviews in Aquaculture, 3(1):3-18.
Singh A.K., (2014). Emerging Alien
Species in Indian Aquaculture: Prospect
And Thereats. Journal of Aquatic Biology
and Fisheries, 2(1):32-41
Strecker AL, Campbell PM, Olden JD
(2011). The aquarium trade as an invasion
pathway in the Pacific northwest. Fisheries
36(2), 74–85.
Suguan VV (1995). Exotic Fishes and their
Role in Reservoir Fisheries in India. FAO
Fisheries Technical Paper No. 345.
Trewavas E (1982). Tilapias: taxonomy
and speciation. In: The biology and culture
of Tilapias. London.
Ujjania N.C., Dubey, M., Sharma, L.L.,
Balai, V.K. and Srivastav, R.M. (2015).
Bio-invasion of exotic fish tilapia
(Oreochromis mossambicus Peters, 1852)
in Lake Jaisamand, India. International
Journal of fisheries and aquatic studies
3(2), 174-177.
Van Zyl B.J., Hay, C.J. and Steyn, G.J.
(1997) The Successful Introduction of
Oreochromis mossambicus in Salt Pans
Along the Namib coast. Madoqua 19(2),
87-89.
Yada T., Hirano, and T. Grou, E.G. (1994)
Changes in Plasma Levels of the Two
Prolactins and Growth Hormones During
Adaptation to Different Salinities in
Euryhaline
Tilapia,
Oreochromis
mossambicus. General and Comparative
Endocrinology 93(2), 214-223.
Under auspices of Environment & Social Welfare Society, India
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