|
Greener
Journal of Agricultural Sciences Vol. 10(3),
pp. 129-135, 2020 ISSN:
2276-7770 Copyright
©2020, the copyright of this article is retained by the author(s) |
|
Helminthes
Load in Two Species of Fish of River Benue: Case Study of Ibi
Fishing Site
Department of Agricultural Technology, Plateau State College
of Agriculture, Garkawa,
|
ARTICLE INFO |
ABSTRACT |
|
Article No.: 0827202110 Type: Research |
This study was undertaken to compare helminthes
parasite load in relation to the sexes of Clarias gariepinus and Oreochromis niloticus of River Benue at Ibi fishing site and their significant differences. A
total of one hundred and fifty two (152) individuals Clarias gariepinus and Oreochromis niloticus
were caught and 76 each in the dry season rainy season. A T-test statistical
analysis was used. Total helminthes load observed
in C. gariepinus
for both seasons was 139.00.
The females had higher helminthes load
(50.36%) while the males had lower (49.64%). Table 2 shows helminthes load of O.
niloticus in both seasons. Total helminthes load observed in O. niloticus for both seasons was 93.00. The females also had higher helminthes load (67.74%) while the males had lower
(32.36%). Total helminthes load observed in both
species was 232.00. The females also
had higher helminthes load (57.33%) while the males
had lower (42.67%). There was no significant difference (p>0.05) in the helminthes load in both species. However, the female had
higher helminthes load (mean: 2.76±0.36) and the male had lower (Mean:
2.58±0.35). There was no significant difference (p>0.05) in the helminthes load in Clarias gariepinus. However, the female had higher
helminthes load (mean: 3.17±0.51) and the male had lower (Mean:
2.28±0.49). There was no significant difference (p>0.05) in the helminthes load in Oreochromis niloticus. However, the female had
higher helminthes load (Mean: 3.05±0.42) and the male had lower (Mean:
2.13±0.44). It may be concluded that helminthes
parasites exist in Clarias gariepinus
and Oreochromis
niloticus of River Benue at Ibi
Fishing Site. Therefore, fish caught in this river should be treated against helminthes parasites. |
|
Accepted: 27/08/2020 Published: 11/09/2020 |
|
|
*Corresponding Author Rabo, P.D. E-mail: phoeberabo29@ gmail.com |
|
|
Keywords: |
|
|
|
|
INTRODUCTION
Fish are the
most diverse groups of vertebrates occupying a variety of marine and freshwater
habitat (DACA, 2006). Fish represent a very important food source providing
comparatively cheap source of animal protein for man and his livestock (Komatsu
and Kitanishi, 2015). Moreover, about a third of the
world population, for example several million people in Africa, depend on fish
for their livelihood from fishing, processing, transporting, and retailing
(World Book, 2001).
Throughout the tropics Claias gariepinus, Oreochromi niloticus, Cyprinus
carpio and Barbus intermedius are the common catches (Ayanda and Egbamuno, 2012; Kawe et al., 2016).
They inhabit calm fresh water ranging from lakes, streams, rivers, swamps to
flood plains many of which are subject to seasonal drying. They survive during
the dry season due to the possession of accessory air breathing organ (Akinsanya and Otubanjo, 2006; Ayanda and Egbamuno, 2012). ).
According to Adewumi and Olaleye
(2011) Clarias gariepinus
hold great prospect for fish farming in Nigeria. These authors emphasized that
the wide geographical spread, high growth rate and the resistance to handling
and stress has made C. gariepinus well valued in a
wide number of African countries. In most part of the world, fish production is
mainly from the wild. As the world population grows, fish resources are being
depleted at an increasing rate as a result of environmental degradation, over
harvesting, pollution thus fish production could no longer meet the demand of
the growing population (Ayanda and Egbamuno, 2012).
According to Biu et al. (2014) and Murray (2005) the low supply of fish has led to increase
in the involvement of stakeholders in aquaculture leading to problems of
overcrowding, poor environmental conditions and pollution thereby reducing the
immunity of fish and higher susceptibility to parasites and diseases. The
occurrence of a wide variety of fish diseases remains a major constraint to
successful economic development (Yimer and Eneyew,
2003). Diseases of fish are known to cause productivity losses from high
mortality, both in aquaculture and extensive inland fisheries aside from being
causes of human diseases in many areas of the world (Biu
et
al., 2014). Kawe et al. (2016) asserted that fish parasites are among the major pathogens,
which cause fish diseases and spoil the appearance of fish thus resulting in
consumer rejection. Several groups of parasites belonging to helminthes,
arthropods and protozoan are known to infect fish and produce harmful effects
on their hosts. Gaherwal et al. (2016) and Omeji
et al. (2013) reported the common helminth parasites of fish are nematodes
(Procamallanus laevionchus
and Rhabdochona congolensis), cestodes
(Polyonchobothrium clariae) and trematodes (Allocreadium spp and Heterophyidae spp). Unfortunately there has not been a well
report of helminthes load of wild fish in the study area; this is why it necessitated
to carry out this study in order to determine the helminthes
load in two species of fish of River Benue: case study of Ibi
Fishing Site.
MATERIALS AND METHODS
Study Area
Ibi is a town
and an administration district in Taraba State,
Nigeria. The town is located on the south bank of the Benue River opposite the
influx of the much smaller Shemankar River. Both the Taraba River and the Donga River flow into the Benue River
within this Local Government Area. The approximate length of the Ibi fishing site is 100km. Ibi
falls within the Northern Guinea Savanna (woody) and the vegetation along the
course of the River is sparse with trees, shrubs and grasses. The coordinate of
Ibi are 80o 19o, 90o
51E/8.317oA N9.850oE having a total land area of 2,672km (1.032sqml) with a
population of 84,054 according to 2006 census (Fig 1 and 2).The climate of the
area consist of two seasons, the rainy season begins at early April and
ends towards the end of October. The dry
season starts from early November to late March. Ibi,
as one of the metrological centers in Taraba State
exhibit a trend of increasing temperature and rainfall with the peak rainfall
in July, August and September; accompanied with flood on both sides of the
river (Oruonye, 2014).The soil consist of sandy loam
soil and clay loam. The extensive flood plain on either side of river
encourages farming activities and important crops include yam, cassava, guinea
corn, maize, tomatoes and beans. Other important anthropogenic activities
include cattle grazing by Fulani, buying and selling of fish (fresh and
smoked), transportation of people and lugages across
the river by boats
Ibi town is made up of predominantly fishermen, fish
sellers, navigators (boat drivers), farmers and business men. Most of the
fisher men are indigenes with a few migrants. The Nwongo
fishing festival is one of the major fishing events in the area. Economic fish
species include Tilapia (Oreochromis niloticus),
Mud fish (Clarias guillaris),
Nile perch (Lates niloticus,),
Silver site (Alestes macroleptilotis), Heterotis niloticus, Polypterus senegalus, Malepterurus electricus, Protopterus annectens, Mormyru srume (Oruonye, 2014).

Figure 1: Map of Nigeria showing Taraba
state with the study area marked in the red rectangular box
Source: Oruonye
(2014)

Figure 2: Survey Map of River Benue at the Ibi fishing Site (100km length of the river)
Source: Oruonye
(2014)
Collection of Specimens
A total of one hundred and fifty two (152) fishes were
used. Fish were collected early in the morning and kept in polythene bags
filled with oxygenated water carefully labeled. All sampling procedures
followed that of Marcogliese (2001). The fish were
transported to the Hydrobiology and Fisheries Laboratory in Zoology Department
of the University of Jos.
Dissection of Fish and Identification of Parasites
Dissection of specimen was done using dissection board
and kit. The body cavity was open following the procedure of Ogbeibu et al.
(2014). Identification of parasites was made following standard keys in
literature Nematodes were cleared with lactophenol
while the cestode and trematodes
were stained overnight with a weak Ehrlich’s haematoxylin
solution and passed through graduated alcohol (30, 50, 70, 90% and absolute)
for 45 min to dehydrate, cleared in methylsalicylate (Amlacher, 2005; Pouder et al., 2011). All parasites collected
were fixed and preserved in 70% ethanol (Amlacher,
2005, Marcogliese, 2001).
Analysis of Data
The data generated was analyzed using descriptive
statistics and t-test was used to to find out the
differences between the sexes of the fish species.
RESULTS
Generally,
the helminthes parasites observed in the fishes were nematodes, cestode and trematodes.
Table 1 shows helminthes load of C. gariepinus
in both seasons. Total helminthes load observed was 139.00.
The females had higher helminthes load
(50.36%) while the males had lower (49.64%).
Table 1: Helminthes parasite load of C. gariepinus in both seasons
|
Sex
|
Number of fish examine |
Parasite Load |
% |
|
Male |
38.00 |
60.00 |
49.64 |
|
Female |
38.00 |
70.00 |
50.36 |
|
Total |
76.00 |
139.00 |
100.00 |
Helminthes
load constitute Nematodes, Cestodes and Trematodes
Table 2 shows helminthes load of O. niloticus in both seasons. Total helminthes load
observed was 93.00. The females also had higher helminthes load (67.74%)
while the males had lower (32.36%).
Table 2: Helminthes parasite load of O. niloticus for both season
|
Sex |
Number of fish examine |
Parasite Load |
% |
|
Male |
38.00 |
30.00 |
32.26 |
|
Female |
38.00 |
63.00 |
67.74 |
|
Total |
76.00 |
93.00 |
100.00 |
Helminthes
load constitute Nematodes, Cestodes and Trematodes
Table 3 shows helminthes load in both
species for both seasons. Total helminthes load observed was 232.00.
The females also had higher helminthes load
(57.33%) while the males had lower (42.67%).
Table 3: Helminthes parasite load in both species for
both seasons
|
Sex |
Number of fish examine |
Parasite Load |
% |
|
Male
|
76.00 |
99.00 |
42.67 |
|
Female |
76.00 |
133.00 |
57.33 |
|
Total |
152.00 |
232.00 |
100.00 |
Helminthes
load constitute Nematodes, Cestodes and Trematodes
Table 4 shows prevalence of helminthes load
in both species for both seasons. There was no significant difference
(p>0.05) in the helminthes load in individual fish. However, the female had
higher helminthes load (mean: 2.76±0.36) and the male had lower (Mean: 2.58±0.35).
Table 4: Prevalence of helminthes parasites in both species for both seasons
|
Sex |
Number of fish examine |
Helminthes
(Mean±SD) |
|
Male |
76 |
2.58±0.35NS |
|
Female |
76 |
2.76±0.36NS |
SD = standard
deviation,
NS Helminthes
load do not differ significantly (P>0.05)
Helminthes
load constitute Nematodes, Cestodes and Trematodes
Table 5 shows prevalence of helminthes load
in Clarias
gariepinus. There was no significant difference
(p>0.05) in the helminthes load in individual fish. However, the female had
higher helminthes load (mean: 3.17±0.51) and the male had lower (Mean: 2.28±0.49).
Table 5: Prevalence of helminthes in Clarias gariepinus.
|
Sex |
Number of fish
examine |
Helminthes (Mean±SD) |
|
Male |
38 |
2.28±0.49NS |
|
Female |
38 |
3.17±0.51NS |
SD = standard
deviation,
NS Helminthes
load do not differ significantly (P>0.05)
Helminthes
load constitute Nematodes, Cestodes and Trematodes
Table 6 shows prevalence of helminthes load
in Oreochromis
niloticus. There was no significant difference
(p>0.05) in the helminthes load in individual fish. However, the female had
higher helminthes load (mean: 3.05±0.42) and the male had lower (Mean: 2.13±0.44).
Table 6: Prevalence of Helminthes in Oreochromis niloticus
|
Sex |
Number of fish
examine |
Helminthes
(Mean±SD) |
|
Male |
38 |
2.13±0.44NS |
|
Female |
38 |
3.05±0.42NS |
SD = standard
deviation
NS Helminthes
load do not differ significantly (P>0.05)
Helminthes
load constitute Nematodes, Cestodes and Trematodes
DISCUSSION
In this
study the percentage prevalence of helminthes parasites in most cases was
higher in the females than males of Clarias
gariepinus and Oreochromis
niloticus obtained from River Benue at Ibi
Fishing Site. However, statistically, there was no significant difference (P>0.05)
observed in the helminthes loads between the males and female This result
agrees supported the report of Olurin and Somorin (2006) who reported no significant difference in
helminthes loads between males and females of Saratherodongalilaeus. However, the
present finding disagrees with the report of Goselle et al. (2008) who reported that female
fish have higher helminthes infection than males. Also, this result is not in
agreement with the report of Kawe et al. (2016) who reported high helminthes
infection in females at 75.29% in C. gariepinus and 73.90% in Tillapia. Zilli. Other scientists like Ohaeri
(2012) and Ukpai (2001) also reported higher
prevalence of helminthes parasites in fish and also higher significant
difference between the males and females with the females having heavy
helminthes load. The influence of sex on the susceptibility of animals to
infestations could be attributed to genetic predisposition and differential
susceptibility owing to hormonal control. The physiological peculiarities of the female animals
constituting stress and lowering the immunity make them vulnerable to
infestation, emaciation and event death (Kawe et al., 2016; Singh et al., 2016).
CONCLUSION
The results
obtained showed that C. gariepinus and O.
niloticus of
River Benue at Ibi fishing site had a prevalence of helminth parasites. For this reason fish caught from this
river should be treated against helminthes parasite.
REFERENCES
Adewumi, A. A . and Olaleye, V. F.
(2011). Catfish culture in Nigeria: Progress, prospects and problems. African Journal of Agricultural Research,
6(6): 1281-1285.
Akinsanya, B. and Otubanjo, O. A. (2006). Helminth Parasites of Clarias gariepinus (Clariidae) in Lekki Lagoon,
Lagos, Nigeria. Revista de Biologia
Tropical, 54(1): 93-99.
Amlacher, E.
(2005). Textbook of Fish Diseases. Narendra Publishing
House, India, 207–
292.
Ayanda, O. I. and Egbamuno, E.
(2012). A Histopathological
examination of the liver and gills of Clarias gariepinus treated with glyphosate. Environmental Research Journal, 6(3):
228-234.
Biu. A. A., Diyaware, M.
Y., Yakaka, W.
and Rita, D. J. (2014). Incidence of Parasites of Clarias gariepinus (Burchell, 1822) Caught from Lake Alau,
Maiduguri, Borno State, Nigeria. Nigerian Journal of Fisheries
and Aquaculture. 2(1): 74-80.
DACA (2006). Standard Veterinary Treatment
Guidelines for Veterinary Clinics. Drug Administration
and Control Authority of Ethiopia (DACA). 1s t
edition, 542.
Gaherwal,
S., Prakash, M. M. and Dudwe,
J. (2016). Incidence and incidence of nematodes in goats at five
different villages of Barwani district, Mathya Pradesh. International
Journal of Advance Resources, 4(3): 1126–1137.
Goselle, O. N., Shir,
G.I.,Udeh, E.O., Abelau, M,
and Imandeh, G.N. (2008).Helminthes parasite of Clarias gariepinus
and Tilapia zilliat Lamingo
Dam Jos, Nigeria. Science world journal,3 (4): 23-24.
Kawe, S. M., God'spower,
R. O., Balarabe M. R. and Akaniru,
R. I. (2016). Prevalence of
gastrointestinal helminth parasites of Clarias gariepinus in
Abuja, Nigeria Sokoto
Journal of Veterinary Sciences, 14(2): 26-33.
Komatsu, K. and Kitanishi, K. (2015).
Household Protein Intake and Distribution of Protein Sources in the Markets of
Southern Ghana: A Preliminary Report. African Study Monograph.,
51(3): 157-173.
Marcogliese, D. J. (2001). Parasites of fish in fresh water;
EMAN, Canada.
Murray, A. G. (2005). A framework for
understanding the potential for emerging diseases. In: aquaculture. Preventive Veterinary Medicine, 67(2-3):
223-235.
Ogbeibu, A. E., Okaka, C. E. and Oribhabor,
B. J. (2014). Gastrointestinal Helminth
parasites community of fish species in the Niger Delta Tidal creck. Journal
of Ecosystem, 1-5.
Ohaeri, C. C. (2012). Gut helminthes parasite and host influences
in Nile tilapia (Oreochromis niloticus). Journal of Biological Science and Conservation, 4: 38-43.
Olurin, K. and somorin,
C. (2006). Intestinal
Helminthes of the Fishes of Owa Stream, South western
Nigeria. Research Journal of Fisheries and Hydrobiology,1,6-9.
Olurin, K., Okafor, J., Alade, A., Asiru, R., Ademiluwa, J., Owonifari, K. and Oronaye, O. (2012). Helminthes parasite of Saratherodon galilaeus and Tilapia zilli
(Pisces: Cichlidae) from River Osun, Southwest Nigeria. International Journal of
Aquatic Science, 3( 2): 49-55.
Omeji, S., Solomon, S. G. and Uloko,
C. (2013). Comparative study on
the Endo-parasitic infestation in Clarias gariepinus collected from earthen and concrete ponds in
Makurdi, Benue State, Nigeria. Journal of Agriculture and Veterinary Science, 2(1): 23-27.
Oruonye, E.
D. (2014). The challenges of fishery resources management practices in Mayo Ranewo community in Ardo Kola
Local Government Area, Taraba State Nigeria. Global Journal of science frontier research,
l4(3): 14-25.
Oruonye, E. D.
(2014). The challenges of fishery resources management practices in Mayo Ranewo community in Ardo Kola
Local Government Area, Taraba State, Nigeria. Global Journal of science frontier research,
l4(3):14-25.
Pounder, D. B., Curtis, E. W. and Yanony, P. E. (2011). Common fresh
water fish parasite pictorial guide Acanthocephelans, leeches
and Pentastome,
University of floride IFAS extension, 1-4.
Singh, R., Kaur,
P., Singla, L. D. and Bal,
M. S. (2016). Prevalence of gastrointestinal parasitism in small ruminant in
western zone of Punjab, India Veterinary World, 10(1): 61-66.
Ukpai, D. H. (2001). Correlations between distribution and abundance are
expected by chance. Journal of
Biodiversity, 18: 463-466.
Yimer, E. and Eneyew, M. (2003). Parasites of fish at Lake Tana. Ethiopia
Journal of Science, 20:31–36.
|
Cite
this Article: Rabo, PD (2020). Helminthes
Load in Two Species of Fish of River Benue: Case Study of Ibi
Fishing Site. Greener Journal of Agricultural Sciences 10(3): 129-135. . |