Research Article | | Peer-Reviewed

Comparison of Specific Ecological Parameters of Nematodes in Six Common Fish Species from the Senegal River and the Gambia River

Received: 11 May 2025     Accepted: 27 May 2025     Published: 30 June 2025
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Abstract

The Senegal River and the Gambia River share the same sedimentary basin, the same source, and have geographical proximity. This study, conducted over three consecutive years in the Senegal River and the Gambia River, aimed to perform a comparative analysis of the prevalence, abundance, mean intensity, and abundance index of nematodes in six fish species common to both locations: Citharinus citharus, Clarias gariepinus, Chrysichthys maurus, Hydrocynus forskahlii, Mormyrops anguilloides, and Synodontis ocellifer. The inventory of parasitic nematodes in these fish revealed that Chrysichthys maurus hosts the highest diversity of parasitic nematodes, with nine genera identified. Citharinus citharus and Mormyrops anguilloides are each parasitized by only one nematode genus, Cithariniella and Contracaecum, respectively. Except of Spirocamallanus and Camallanus, which were found exclusively in C. maurus, most nematode genera are shared among the different fish hosts. The genus Anisakis exhibits the highest prevalence, with 29.03% in the Senegal River, while Cithariniella shows the highest abundance, mean intensity, and abundance index. Other nematode genera, such as Paracamallanus, Procamallanus, Rhabdochona, Contracaecum, Spirocamallanus, Spinitectus, and Falcaustra, display variable ecological parameters. These nematodes are distributed within the liver and various sections of the digestive tract.

Published in Ecology and Evolutionary Biology (Volume 10, Issue 2)
DOI 10.11648/j.eeb.20251002.12
Page(s) 104-114
Creative Commons

This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited.

Copyright

Copyright © The Author(s), 2025. Published by Science Publishing Group

Keywords

Fish, Nematodes, Prevalence, Abundance, Mean Intensity, Abundance Index

1. Introduction
Several studies on the distribution of African freshwater fish have shown that ichthyofauna is unevenly distributed across the continent over geological time. In fact, continental aquatic biodiversity is the result of a long evolutionary history of species, shaped by climate and geomorphological changes .
Senegal and The Gambia are two geographically, economically, socially, and culturally close countries. The Senegal and Gambia Rivers, which flow through these nations, are located within the same Senegal-Mauritanian sedimentary basin, extending from Mauritania to Guinea-Bissau. Both rivers originate in the Fouta-Djallon highlands in Guinea and flow into the Atlantic Ocean . Given these similarities, the two rivers are likely to share several fish species that may host the same parasites.
The aim of this study is to inventory several fish species common to both the Senegal and Gambia Rivers and their parasitic nematodes. We note that the fish studied in this work are infected with several other groups of parasites. However, we specialize in the study of nematodes to ensure continuity. Indeed, in Senegal, several authors have studied fish nematodes . Therefore, this current work adds to the many studies already carried out. It seeks to evaluate ecological parameters, including prevalence (P), abundance (A), mean intensity (MI), and the specific dominance index (DI) of parasitic nematodes, based on location, season, and host sex. Additionally, the study assesses the relationships between prevalence and the infestation sites of nematodes. These results will also allow us to establish a correlation between parasitic nematodes in fish and those in humans, and to determine the times of year when parasitism is highest.
2. Materials and Methods
The fish were collected at Richard-Toll (16°27′31.96″ N, 15°41′38.56″ W) on the Senegal River (S) and at Gouloumbou (13°34′58.82″ N, 13°41′44.21″ W), a Senegalese territory located on the Gambia River (G). The following map shows the sampling locations.
Figure 1. Geographical distribution of sampling locations.
Fish sampling was carried out randomly between 2018 and 2021 during both the rainy and dry seasons and in two different localities, the Senegal River and the Gambia River . The fish specimens were transported to Cheikh Anta Diop University in Dakar, specifically to the Animal Biology Department within the Faculty of Science and Technology.
Fish identification was performed according to . Dissection enabled determination of sex and collection of nematodes from various organs (stomach, intestine, rectum, and liver). These roundworms were subsequently preserved in 70% ethanol and examined using a Nikon optical microscope.
Statistical Analysis
We calculated prevalence, mean abundance, dominance index and mean intensity following the methodology of . Ecological terms:
Prevalence is given by the following formula:
P (%) = N/H * 100
Where (N) is the number of hosts infested by a parasite species and (H) is the number of fish examined.
The average abundance (A) corresponds to the total number of individuals of a parasite species (n) out of the total number of individuals examined (H).
A = n/H
The average intensity is the total number of parasites of a particular species found in a sample divided by the number of hosts infected by that parasite.
MI = n/N
Where (n) is the total number of individuals of a parasite species and (N) is the number of infested hosts.
The dominance index corresponds to the percentage ratio of the number of individuals of a parasite species (n) to the total number of individuals (all species combined) (Ni).
DI (%) = n/Ni * 100
Data entry and statistical computations were performed using R software (version 4.0.0) and Microsoft Word (2016).
3. Results
The Senegal River and Gambia River exhibit substantial ichthyological diversity. Among their fish communities, six species were common to both systems: Citharinus citharus, Clarias gariepinus, Chrysichthys maurus, Hydrocynus forskahlii, Mormyrops anguilloides, and Synodontis ocellifer. A total of 749 fish specimens were collected. Table 1 presents the distribution of host fishes by sex, location, and seasonal variation.
Table 1. Distribution of Host Fish by Sex, Locality, and Season.

Host Fishes

Senegal River

Gambia River

Dry season

wet season

Dry season

wet season

Male

Female

Male

Female

Male

Female

Male

Female

Citharinus citharus Geoffroy Saint-Hilaire, 1809

29

34

30

18

21

18

39

25

Clarias gariepinus Burchell, 1822

17

9

13

12

0

0

15

16

Chrysichthys maurus Valenciennes, 1840

37

29

0

0

21

22

27

37

Hydrocynus forskahlii Cuvier, 1819

19

21

22

23

26

23

21

14

Mormyrops anguilloides Linnaeus, 1758

0

21

0

0

22

14

0

0

Synodontis ocellifer Boulenger, 1900

13

13

0

0

13

15

0

0

A total of 360 fish were sampled in the Senegal River compared to 339 in the Gambia River. The dry season sampling yield was higher in the Senegal River than in the Gambia River, while the reverse pattern was observed during the rainy season. Overall, fish catch numbers were significantly greater during the dry season than the rainy season (t-test, p<0.05). This likely reflects increased fish availability during low water levels caused by seasonal evaporation.
Male fish specimens outnumbered females across all sampling locations and seasons. Citharinus citharus, Chrysichthys maurus, and Hydrocynus forskahlii were the most abundantly represented species, forming the dominant taxa at all collection sites.
Following nematode collection, parasitological metrics (prevalence, abundance, mean intensity, and dominance index) were calculated and summarised in Table 2.
Table 2. Site-Specific Parameters by Locality.

Nematode Species

Site-Specific Ecological Parameters

Prevalence (%)

Mean Abundance

Mean parasitic intensity

Dominance Index (%)

Senegal River

Gambia River

Senegal River

Gambia River

Senegal River

Gambia River

Senegal River

Gambia River

C. citharus

Cithariniella citharini Khalil, 1964

9,91

-

1,243

-

12,545

-

100

-

Cithariniella sp

-

27,885

-

5,442

-

19,517

-

100

C. gariepinus

Contracaecum larvae

6.452

0

0.839

0

13

0

6.046

0

Paracamallanus sp

0

12,903

0

0,613

0

4,75

0

90,476

Procamallanus laeviconchus Wedl, 1862

16,129

-

2,613

-

16,2

-

18,837

-

Procamallanus sp

-

9,524

-

0,064

-

1

-

9,524

Anisakis larvae

29,03

0

4,37

0

15,05

0

0,6

0

C. maurus

Cithariniella khalili Petter and al., 1972

0

2,062

0

0,062

0

3

0

9,231

Paracamallanus sp

0

1,031

0

0,01

0

1

0

1,538

Procamallanus sp

0

9,278

0

0,319

0

3,444

0

47,692

Larvae of Rhabdochona sp

0

1,031

0

0,01

0

1

0

1,538

Contracaecum larvae

1,316

2,062

0,131

0,021

10

1

100

3,077

Anisakis larvae

0

1,031

0

0,144

0

14

0

21,538

Spirocamallanus sp

0

2,062

0

0,144

0

1

0

3,077

Spinitectus sp

0

1,031

0

0,01

0

1

0

1,538

Larvae of Falcaustra guiersi Vassilades, 1973

0

2,062

0

0,062

0

3

0

9,231

Camallanus ctenopomae Petter (1972).

0

1,031

0

0,01

0

1

0

1,538

H. forskahlii

Rhabdochona sp

3,158

2,703

0,031

0,392

1

3,222

100

60,417

Contracaecum larvae

0

4,054

0

0,216

0

5,333

0

33,333

Spinitectus sp

0

1,351

0

0,027

0

2

0

4,167

Anisakis larvae

0

1,351

0

0,013

0

1

0

2,083

M. anguilloides

Contracaecum larvae

0

7,692

0

0,077

0

1

0

100

S. ocellifer

Cithariniella khalili Khalil, 1964

0

7,143

0

0,178

0

2,5

0

6,097

Spinitectus sp

0

3,571

0

0,036

0

1

0

1,219

Falcaustra guiersi Vassilades, 1973

0

42,857

0

2,714

0

6,333

0

92,683

Procamallanus laeviconchus Wedl, 1862

7,692

0

0,385

0

5

0

90.90

0

Contracaecum larvae

3,846

0

0,038

0

1

0

9.909

0

Citharinus citharus exclusively harboured nematodes of the genus Cithariniella. Prevalence, abundance, and mean intensity values were significantly higher in the Gambia River for Cithariniella sp. (Fisher, pvalue =8.079e-07), whereas the Senegal River population was parasitised solely by Cithariniella citharini.
In the Gambia River, C. gariepinus were parasitised by Contracaecum and Anisakis larvae, alongside nematodes of the genus Procamallanus. In the Senegal River the fish harboured Procamallanus infections, with significantly higher parasitological metrics (prevalence, abundance, and intensity) for Procamallanus laeviconchus in the Senegal River (Fisher, p < 1.2e-15). The Gambia River specimens additionally hosted Paracamallanus sp.
Chrysichthys maurus harboured nematodes from ten genera, though only Contracaecum occurred in both river systems. Contracaecum exhibited significantly higher abundance, mean intensity, and dominance index in the Senegal River (p < 0.01), while prevalence was greater in the Gambia River (p = 0.017).
Four nematode genera parasitise Hydrocynus forskahlii: Rhabdochona, Contracaecum, Spinitectus, and Anisakis. Rhabdochona occurred in both river systems, with significantly higher prevalence, abundance, and intensity in the Senegal River (p < 0.05). In contrast, Contracaecum, Spinitectus, and Anisakis were restricted to H. forskahlii populations in the Gambia River.
Mormyrops anguilloides was parasitised exclusively by Contracaecum sp. in the Gambia River. In Synodontis ocellifer, three nematode taxa (Cithariniella khalili, Spinitectus sp., and Falcaustra guiersi) were restricted to the Gambia River population, while the Senegal River population hosted Procamallanus laeviconchus and Contracaecum sp. larvae.
Seasonal ecological parameter calculations are summarised in Table 3.
Table 3. Season-Specific Parameters.

Nematode Species

Season-Specific Ecological Parameters

Prevalence (%)

Mean Abundance

Mean Intensity

Dominance Index (%)

Dry Season

Rainy Season

Dry Season

Rainy Season

Dry Season

Rainy Season

Dry Season

Rainy Season

G

S

G

S

G

S

G

S

G

S

G

S

G

S

G

S

C. citharus

Cithariniella citharini Khalil, 1964

4.76

16.66

0.34

2.41

7.33

14.5

1

1

Cithariniella sp.

100

0

24.93

0

24.93

0

1

0

C. gariepinus

Contracaecum larvae

0

7.69

0

0

0

1

0

0

0

13

0

0

0

6.04

0

0

Paracamallanus sp.

0

0

12.9

0

0

0

0.61

0

0

0

4.75

0

0

0

0.9

0

Procamallanus laeviconchus Wedl, 1862

19.23

0

3.11

0

16.2

0

1

0

Procamallanus sp.

0

6.45

0

0.06

0

1

0

0.09

Anisakis larvae

29,03

0

0

0

4,37

0

0

15,05

0

0

0

0,6

0

0

C. maurus

Cithariniella khalili Petter and al., 1972

0

0

3.12

0

0

0

0.09

0

0

0

3

0

0

0

0.09

0

Paracamallanus sp.

0

0

1.56

0

0

0

1.56

0

0

0

1

0

0

0

0.01

0

Procamallanus sp.

0

0

14.06

0

0

0

0.48

0

0

0

3.44

0

0

0

0.5

0

Larvae of Rhabdochona sp.

0

0

1.56

0

0

0

0.015

0

0

0

1

0

0

0

0.016

0

Contracaecum larvae

6.06

1.31

0

0

0.06

0.13

0

0

1

10

0

0

0.66

1

0

0

Anisakis larvae

0

0

1.56

0

0

0

0.21

0

0

0

14

0

0

0

0.22

0

Spirocamallanus sp.

0

0

3.12

0

0

0

0.03

0

0

0

1

0

0

0

0.03

0

Spinitectus sp.

0

0

1.56

0

0

0

0.01

0

0

0

1

0

0

0

0.01

0

Larvae of Falcaustra guiersi Vassilades, 1973

0

0

3.12

0

0

0

0.09

0

0

0

3

0

0

0

0.09

0

Camallanus ctenopomae Petter (1972).

3.03

0

0

0

0.03

0

0

0

1

0

0

0

0.3

0

0

0

H. forskahlsg7ii

Rhabdochona sp.

6.12

3.33

24

3.07

0.28

0.03

0.6

0.03

4.66

1

0.4

2

0.46

1

0.83

2

Contracaecum larvae

4.08

0

4

0

0.28

0

0.08

0

7

0

2

0

0.46

0

0.11

0

Spinitectus sp.

2.04

0

0

0

0.04

0

0

0

2

0

0

0

0.06

0

0

0

Anisakis larvae

0

0

4

0

0

0

0.04

0

0

0

1

0

0

0

0.05

0

M. anguilloides

Contracaecum larvae

7.40

0

0

0

0.07

0

0

0

1

0

0

0

1

0

0

0

S. ocellifer

Cithariniella khalili Khalil, 1964

7.14

0

0

0

0.17

0

0

0

2

0

0

0

0.06

0

0

0

Spinitectus sp.

3.5

0

0

0

0.03

0

0

0

1

0

0

0

0.01

0

0

0

Falcaustra guiersi Vassilades, 1973

42.85

0

0

0

2.71

0

0

0

6.33

0

0

0

0.92

0

0

0

Procamallanus laeviconchus Wedl, 1862

0

7.69

0

0

0

0.38

0

0

0

5

0

0

0

0.9

0

0

Contracaecum larvae

0

3.8

0

0

0

0.03

0

0

0

1

0

0

0

0.09

0

0

In C. citharus, nematodes of the genus Citharinella show higher prevalence, abundance, and mean intensity in the Gambia River during the dry season, particularly Cithariniella sp. The dominance index remains constant and equal to 1 at both sampling sites. However, during the rainy season, these parameters drop to zero in the Gambia River. In contrast, in the Senegal River, Cithariniella citharini displays higher prevalence, abundance, mean intensity, and dominance index during the rainy season compared to the dry season.
In C. gariepinus, the genus Paracamallanus was present during the rainy season in the Gambia River (Paracamallanus sp.), whereas Anisakis occurred in the Senegal River during the dry season. This host also harboured Procamallanus spp. year-round, though infection parameters (prevalence, abundance, intensity) were higher for Procamallanus laeviconchus in the Senegal River.
In C. maurus, the nematodes Cithariniella khalili, Paracamallanus sp., Procamallanus sp., larval Rhabdochona sp., Anisakis, Spirocamallanus sp., Spinitectus sp., and larval Falcausatra guiersi were absent during the dry season but present exclusively in the Gambia River during the rainy season. In contrast, larval Contracaecum occurred only in the dry season, with higher infection parameters in the Gambia River. The nematode Camallanus ctenopomae parasitised C. maurus solely in the dry season and only in the Senegal River.
In H. forskahlii, Rhabdochona sp. was present year-round in both rivers, with higher prevalence in the Gambia River. Larval Contracaecum and Spinitectus sp. were also detected in H. forskahlii in the Gambia River, but only during the dry season, with Contracaecum exhibiting higher infection metrics. Anisakis was restricted to the Gambia River and occurred exclusively in the rainy season.
In S. ocellifer, nematodes of the genera Contracaecum, Citharinella, Spinitectus and Falcaustra were present exclusively during the dry season in the Gambia River, with higher infection parameters observed for Falcaustra guiersi. However, Procamallanus laeviconchus and larval Contracaecum occurred only in the Senegal River during the dry season.
The calculation of prevalence, abundance, mean intensity and dominance index by sex yielded the following results (Table 4).
Table 4. Sex-Specific Parameters.

Host Fish

Nematode species

Gender-specific ecological parameters

Prevalence (%)

Abundance

Mean Intensity

Dominance Index (%)

Male

Female

Male

Female

Male

Female

Male

Female

G

S

G

S

G

S

G

S

G

S

G

S

G

S

G

S

C. citharus

Cithariniella citharini Khalil, 1964

11,86

7,69

1,10

1,40

9,28

18,25

100

100

Cithariniella sp.

29,58

25

5,89

4,62

19,90

18,5

100

100

C. gariepinus

Contracaecum larvae

0

10

0

0

0

1.3

0

0

0

13

0

0

0

9.48

0

0

Paracamallanus sp.

20

0

6,25

0

0,87

0

0,37

0

4,33

0

6

0

86,67

0

100

0

Procamallanus laeviconchus Wedl, 1862

20

9,09

3,4

1,18

17

13

24,82

8,33

Procamallanus sp.

13,33

0

0,13

0

1

0

13,33

0

Aanisakis larvae

0

55

0

63,63

0

7,2

0

11,54

0

13,09

0

18,14

0

0,52

0

0,81

C. maurus

Cithariniella khalili Petter and al., 1972

2,08

0

2,04

0

0,08

0

0,04

0

4

0

2

0

13,33

0

5,71

0

Paracamallanus sp.

2,08

0

0

0

0,02

0

0

0

1

0

0

0

3,33

0

0

0

Procamallanus sp.

6,25

0

12,24

0

0,12

0

0,51

0

2

0

4,17

0

20

0

71,43

0

Larvae of Rhabdochona sp.

2,08

0

0

0

0,02

0

0

0

1

0

0

0

3,33

0

0

0

Larvae of Contracaecum

0

0

4,08

3,45

0

0

0,04

0,34

0

0

1

10

0

0

2,86

100

Anisakis larvae

2,08

0

0

0

0,29

0

0

0

14

0

0

0

46,67

0

0

0

Spirocamallanus sp.

2,08

0

2,17

0

0,02

0

0,02

0

1

0

1

0

3,33

0

2,86

0

Spinitectus sp.

0

0

2,17

0

0

0

0,02

0

0

0

1

0

0

0

2,86

0

Larvae of Falcaustra guiersi Vassilades, 1973

2,08

0

2,17

0

0,06

0

0,06

0

3

0

3

0

10

0

8,57

0

Camallanus ctenopomae Petter (1972).

0

0

2,17

0

0

0

0,02

0

0

0

1

0

0

0

2,86

0

H. forskahlii

Rhabdochona sp.

10,81

1,96

13,51

4,54

0,30

0,02

0,49

0,04

3

1

3,6

1

91,67

100

50

100

Contracaecum larvae

0

0

8,11

0

0

0

0,43

0

0

0

5,33

0

0

0

43,24

0

Spinitectus sp

0

0

2,70

0

0

0

0,54

0

0

0

2

0

0

0

5,56

0

Anisakis larvae

2,70

0

0

0

0,03

0

0

0

1

0

0

0

8,33

0

0

0

M. anguilloides

Contracaecum larvae

0

0

14,28

0

0

0

0,14

0

0

0

0

0

0

0

100

0

S. ocellifer

Cithariniella khalili Khalil, 1964

7,69

0

6,67

0

0,31

0

0,07

0

4

0

1

0

15,38

0

1,78

0

Spinitectus sp.

0

0

6,67

0

0

0

0,07

0

0

0

1

0

0

0

1,78

0

Falcaustra guiersi Vassilades, 1973

23,08

0

60

0

1,69

0

3,6

0

0

7,33

6

0

84,61

0

96,43

0

Procamallanus laeviconchus Wedl, 1862

0

0

0

15,38

0

0

0

0,77

0

0

0

5

0

0

0

90,91

Contracaecum larvae

0

0

0

7,69

0

0

0

0,08

0

0

0

1

0

0

0

9,09

Nematodes of the genus Citharinella exhibited higher prevalence in male C. citharus, particularly within the Gambia River. In C. gariepinus, Paracamallanus sp. infections were more frequent in males from the Gambia River, while Procamallanus spp. were absent in females from the same location. Male C. gariepinus showed elevated infection parameters for Paracamallanus and Procamallanus, whereas Anisakis metrics were significantly higher in females.
For C. maurus, Cithariniella khalili, Paracamallanus sp., Procamallanus sp., Rhabdochona sp., Spirocamallanus sp., and larval stages of Falcaustra guiersi and Anisakis occurred exclusively in the Gambia River, with males displaying higher infection parameters - except for Procamallanus which showed female-biased infections. Larval Contracaecum, Spinitectus sp. and Camallanus ctenopomae were absent in males but present in females from this river.
In H. forskahlii, females demonstrated significantly greater prevalence, abundance, mean intensity and dominance indices than males, particularly in Gambia River specimens. Larval Contracaecum and Spinitectus sp. infections were restricted to females in the Gambia River, while Anisakis occurred exclusively in males.
Figure 2. Distribution of nematodes in the organs of host poisons.
Certain fish organs exhibited particularly high nematode densities. The rectum of C. citharus (primarily infected by Citharinella spp.) and the liver of C. gariepinus (dominated by Anisakis spp.) showed the heaviest parasite loads. Conversely, other organs demonstrated lower infestation rates, including the intestines of C. citharus and M. anguilloides, and the liver of H. forskahlii.
Moderate parasite burdens were observed in C. maurus and S. ocellifer, though their intestinal tracts consistently harboured higher nematode numbers than other organs. Notably, parasite biodiversity did not correlate with infection intensity - hosts with the highest worm burdens were typically infected by just a single genus.
4. Discussion
Our findings demonstrate that only nematodes of the genus Citharinella parasitize C. citharus, observed across all sampled fish from both localities and during both seasons. This aligns with the work of , who described three Cithariniella species (C. citharini, C. khalili, and C. gonzalesi) in fish collected in November, shortly after the rainy season in Senegal. Notably, C. citharini infecting C. citharus exhibited a prevalence of 60%. In contrast, reported a lower prevalence of 10% in the same host species sampled between May and November in Nigeria, suggesting spatial and temporal variability in infection dynamics.
Our results further highlight seasonal and geographical variations in prevalence, with the Gambia River showing higher infection rates during the dry season. This pattern may be linked to host migratory behaviour. Indeed, identified Citharinus citharus as a migratory species, moving in response to flood and drought cycles. documented its seasonal dispersal from Lake Guiers to the Senegal River during flood periods, which could facilitate the species' broad geographical distribution and explain observed prevalence fluctuations.
Clarias gariepinus was found to host nematodes of the genera Procamallanus, Paracamallanus, and Anisakis. These findings align with previous reports from various African localities . Notably, our specimens exhibited higher Procamallanus infection rates during the dry season, consistent with observations by .
While most aforementioned studies reported no significant sex-based differences in infection rates for C. gariepinus, our data revealed male-biased parasitism for both Procamallanus and Paracamallanus. This discrepancy may reflect regional variations in host ecology or parasite transmission dynamics.
Regarding organ distribution, documented heavier intestinal infections by adult Procamallanus and Paracamallanus nematodes, while reported the first occurrence of these genera in bile vesicles. Contrasting with our findings, neither study detected nematodes in liver tissue, suggesting potential differences in parasite tropism across host populations or geographical regions.
In H. forskahlii, four nematode genera (Rhabdochona, Contracaecum, Spinitectus, and Anisakis) were identified in specimens from the Gambia River, while only Rhabdochona was found in those from the Senegal River. This genus was similarly reported by in Lake Turkana, Kenya. The observed disparity in parasite diversity between rivers may reflect differences in food web complexity, with more diverse infection sources likely existing in the Gambia River system.
Contracaecum emerged as the most prevalent nematode genus in H. forskahlii, consistent with findings by , and . However, our study recorded lower and seasonally stable prevalence rates for this genus, contrasting with the significantly higher values reported by and . Notably, we observed sex-biased infection patterns, with females showing higher prevalence, mean intensity, and abundance of Contracaecum - a finding that aligns with 's results.
Certain nematodes are common to specific hosts. Indeed, the genus Contracaecum parasitises S. ocellifer, M. anguilloides, and C. maurus. Its prevalence and abundance are higher in M. anguilloides, while its mean intensity is higher in C. maurus. It is also the only nematode found in M. anguilloides, where Dujardinascaris mormyropsis has been reported by . The genera Cithariniella, Spinitectus, Falcaustra, and Procamallanus are also common to S. ocellifer and C. maurus. The prevalence and abundance of the genera Cithariniella, Spinitectus, and Falcaustra are higher in S. ocellifer, whereas the genus Procamallanus exhibits higher parameters in C. maurus. These nematode genera have also been reported by other authors in various hosts. Thus, reported the genus Contracaecum in Synodontis nigrita, while demonstrated the presence of the genera Procamallanus and Citharinella in Synodontis schall and Synodontis nigrita. reported the presence of the genera Rhabdochona, Spinitectus, and Procamallanus in Synodontis schall and Synodontis bentosoda. In contrast, other nematode genera are host-specific. This is the case for Paracamallanus and Camallanus, which are found exclusively in C. maurus. Their presence could be explained by a combination of biological, ecological, and evolutionary factors that interact dynamically to establish highly specialised relationships between the nematode and its host. Regarding infestation sites, they are diverse and vary according to the nematode's developmental stage, corresponding to specific areas adapted to the morphology and feeding physiology of the nematodes. Indeed, adult nematodes typically colonise the intestine and stomach, while larvae are found in the body cavity or in certain organs such as the kidney and liver.
Thus, in C. gariepinus, various body parts can be infected by parasites. The intestine and stomach are the most frequently parasitised organs, as shown by our results, which are consistent with those of . However, other organs can also harbour nematodes, such as the rectum or the skin .
The intestine and stomach are the most frequently parasitised organs in H. forskahlii and M. anguilloides. Indeed, nematodes encyst within the intestinal wall or remain free in the intestinal lumen, as shown by the work of. They can also be found on the stomach wall . Other organs, such as the liver, can also be infected.
In C. citharus, the rectum is the most frequently parasitised organ, confirming the findings of and . However, other parts of the digestive tract can also harbour nematodes, such as the oesophagus, intestine, and stomach, as reported by .
Abbreviations

P

Prevalence

A

Abundance

MI

Mean Intensity

DI

Dominance Index

S

Senegal River

G

Gambia River

Conflicts of Interest
The author declares no conflicts of interest.
References
[1] Akinsanya, B., & Otubanjo, O. A. Helminth Parasites of Clarias gariepinus (Clariidae) in Lekki Lagoon, Lagos, Nigeria. Rev. Biol. Trop. (Int. J. Trop. Biol. ISSN-0034-7744). 2005, Vol. 54 (1): 93-99.
[2] Aliyu, M. D., & Solomon, J. R. The intestinal parasite of Clarias gariepinus found at lower Usman Dam, Abuja. Researcher. 2016. 2012; 4(9).
[3] Ayanda, O. I. Comparative parasitic helminth infection between cultured and wild species of Clarias gariepinus in Ilorin, North – Central Nigeria. Scientific Research and Essay. 2008, Vol. 4 (1): 018-021. URL:
[4] Dougnon, J., Montchowui, E., Daga, F. D., Houessionon, J., Laléyé, P., & Sakiti, N. Cutaneous and Gastrointestinal Helminth Parasites of the Fish Synodontis schall and Synodontis nigrita (Siluriformes: Mochokidae) from the Lower Ouémé Valley in South Benin. Research Journal of Biological Sciences. 2012, 7 (8): 320-326. URL:
[5] Eyo, J. E.., Iyaji, F. O., & Obiekezie, A. I. Parasitic infestation of Synodontis batensoda (Rüppell, 1832, Siluriformes, Mockokidae) at Rivers Niger-Benue Confluence, Nigeria. African Journal of Biotechnology. 2012, Vol. 12(20), p 3029-3039, 15.
[6] Hopson, A. J. Lake Turkana. A report on the findings of the Lake Turkana Project 1972-1975. London, Overseas Development Administration. nhml_london; biodiversity. 1982, 6 vol., 1614 p.
[7] Division. National Institute for Freshwater Fisheries Research (NIFFR), P. M. B. 6006, New Bussa, Niger State, Nigeria. (2005). Investigation of nematode Eustrongylides larvae infections in mudfish Clarias gariepinus and C. anguillaris from Bida floodplain of Nigeria. Aquatic Pathobiology Programme, Artisanal Fisheries Division, Sociology Programme, Socio-Economics and Extension Division, Programme Socio-Economics and Extension. Available from:
[8] Iyabo, U. B. Gut Helminth Parasites of Citharinus citharus in Anambra River Flood System, Southeastern Nigeria. American Journal of Agricultural Science. 2015, 2(2): 63-69. URL:
[9] Iyaji, F. O., & Yaro, C. A. Endoparasitic helminths of Synodontis schall (Bloch and schneider, 1801, siluriformes, mochokidae) at the confluence of Niger and Benue Rivers, Lokoja, Nigeria. International Journal of Fisheries and Aquatic Studies. 2016, 4(5): 30-35. URL:
[10] Koubková, K., Baruš, V. & Hodova, I. Nematodes of Cithariniella (Pharyngodonidae) from freshwater fishes in Senegal, with a key to species. Helminthologia. 2010, 47, 2: 105-114.
[11] Lamagat, J. P., Albergel, J., Bouchez, J. M., & Descroix, L. Monographique Hydrologique du Fleuve Gambie. Institut français de recherche scientifique pour le développement (ORSTOM) en coopération avec l’organisation pour la mise en valeur du fleuve Gambie (OMVG). 1990, 257 pages.
[12] Lévêque, C., & Paugy, D. Les poissons des eaux continentales africaines. Diversité, écologie, utilisation par l’homme. Institut pour la Recherche et pour le Développement, IRD. 2006, Pages 67-172-173-194-218.
[13] Lévêque, C., Bruton, M. N., & Ssentongo, G. W. Biologie et Ecologie des Poissons d’Eau Douce Africains. ORSTOM Editeur. Nº 30487. 1988.
[14] Lévêque, C., Paugy, D., &. Teugels, G. G. Faune des poissons d'eaux douces et saumâtres d'Afrique de l'Ouest. Editions de I'ORSTOM Paris. Institut Français de Recherche Scientifique pour le Développement en Coopération. Collection Faune tropicale no XXVlll, TOME 1. 1990, 386 Pages.
[15] Mabika, N., Barson, M., Dyk, C. V., & A. Oldewage, A. Taxonomy, distribution and prevalence of parasites of tigerfish, Hydrocynus vittatus (Castelnau, 1861) in the Sanyati basin, Lake Kariba, Zimbabwe. Acta Parasitologica. 2016, 61(3): 614-620.
[16] Makeri, V. A., Annune, P. A., & Cheikyula, J. O. Seasonal Variation in Endoparasite Loads in Four Fish Species from Lower River Benue, Makurdi Nigeria. Asian Journal of Basic Science & Research. 2020, Volume 2, Issue 2, Pages 37-43.
[17] Moravec, F., & Jirků, M. Dujardinascaris mormyropsis n. sp. (Nematoda: Anisakidae) from the osteoglossiform fish Mormyrops anguilloides (Linnaeus) (Mormyridae) in Central Africa. Systematic Parasitology. 2014, Volume 88, pages 55–62.
[18] Moravec, F., Charo-Karisa, H., & Jirků, M. The morphology and systematics of Rhabdochona paski Baylis, 1928 (Nematoda: Rhabdochonidae), a widespread parasite of freshwater fishes in Africa. Systematic Parasitology. 2013, Volume 85, pages 55–63.
[19] Petter, A. J., Vassiliades, G., & Troncy, P. M. Trois espèces d’Oxyures parasites de Poissons en Afrique. Annales de Parasitologie (Paris). 1972, t. 47, n° 4, pp. 569 à 579. URL:
[20] Rochette, C., & Touchebeuf, P. Aperçue Hydrologique du fleuve Sénégal. Office de la Recherche Scientifique et Technique Outre-Mer (O.R.S.T.O.M.); 1964 125 Pages.
[21] Seck, C. M. B., Dione, E. N. M., & Diouf, M. Study of some ecological parameters in nematode parasites of freshwater fish in the Senegal and Gambia rivers. International Journal of Fisheries and Aquatic Studies. 2024, 12(3): 76-83.
[22] Sedogbo, M. H., Zannou, B T., Siko, J. E, Tossavi, N. D., Togla, I., Fiogbe, E. D., & Ibikounle, M. Faune des métazoaires parasites de Clarias gariepinus (Clariidae) et de Oreochromis niloticus (Cichlidae), deux poissons des whédos du delta supérieur du fleuve Ouémé au sud du Bénin. Int. J. Biol. Chem. Sci. 2019, 13(2): 983-997.
[23] Sorour, Sh. S., & Hamouda, A. H. Prevalence of nematodes infestation in Clarias gariepinus from El-Burullus Lake and Lake Nasser, Egypt. Iraqi Journal of Veterinary Sciences. 2019, Vol. 33, No. 2, pp. 181-188. 9 pages.
[24] Toluhi, O. O., & Adeyemi, S. O. Helminth parasites of Synodontis nigrita at lower Niger (IDAH), Nigeria. Africain Journal of Biotechnology. 2010, Vol. 12(51), 7120-7123.
[25] Younis, A. E., Saad, A. I., & Rabei, J. M. The occurrence of Contracaecum sp. larvae (Nematoda: Anisakidae) in four teleostean species from Lake Nasser, Egypt: morphological and molecular studies. The Journal of Basic and Applied Zoology. 2017, 78: 9.
[26] Margolis L., Esch G. W., Holmes J. C., Kuris A. M. & Schad G. A. The Use of Ecological Terms in Parasitology (Report of an Ad Hoc Committee of the American Society of Parasitologists). The Journal of Parasitology. 1982, Vol. 68, No. 1, 131-133 (3 pages).
[27] Otachi, E. O., Körner, W., & Avenant-Oldewage, A. Trace elements in sediments, blue spotted tilapia Oreochromis leucostictus (Trewavas, 1933) and its parasite Contracaecum multipapillatum from Lake Naivasha, Kenya, including a comprehensive health risk analysis. Environ Sci Pollut Res. 2014, 21, 7339–7349.
[28] Iboh C. I., & Ajang R. O. Helminths parasitics infection of Clarias gariepinus from great kwa river, cross river Nigeria. European Journal of Pharmaceutical and Medical Research. 2016, 3(12), 101-105.
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    Seck, C. M. B., Dione, E. N., Diouf, M. (2025). Comparison of Specific Ecological Parameters of Nematodes in Six Common Fish Species from the Senegal River and the Gambia River. Ecology and Evolutionary Biology, 10(2), 104-114. https://doi.org/10.11648/j.eeb.20251002.12

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    Seck, C. M. B.; Dione, E. N.; Diouf, M. Comparison of Specific Ecological Parameters of Nematodes in Six Common Fish Species from the Senegal River and the Gambia River. Ecol. Evol. Biol. 2025, 10(2), 104-114. doi: 10.11648/j.eeb.20251002.12

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    AMA Style

    Seck CMB, Dione EN, Diouf M. Comparison of Specific Ecological Parameters of Nematodes in Six Common Fish Species from the Senegal River and the Gambia River. Ecol Evol Biol. 2025;10(2):104-114. doi: 10.11648/j.eeb.20251002.12

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  • @article{10.11648/j.eeb.20251002.12,
      author = {Cheikh Mouhamadou Bamba Seck and Ephigénie Ndew Dione and Malick Diouf},
      title = {Comparison of Specific Ecological Parameters of Nematodes in Six Common Fish Species from the Senegal River and the Gambia River
    },
      journal = {Ecology and Evolutionary Biology},
      volume = {10},
      number = {2},
      pages = {104-114},
      doi = {10.11648/j.eeb.20251002.12},
      url = {https://doi.org/10.11648/j.eeb.20251002.12},
      eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.eeb.20251002.12},
      abstract = {The Senegal River and the Gambia River share the same sedimentary basin, the same source, and have geographical proximity. This study, conducted over three consecutive years in the Senegal River and the Gambia River, aimed to perform a comparative analysis of the prevalence, abundance, mean intensity, and abundance index of nematodes in six fish species common to both locations: Citharinus citharus, Clarias gariepinus, Chrysichthys maurus, Hydrocynus forskahlii, Mormyrops anguilloides, and Synodontis ocellifer. The inventory of parasitic nematodes in these fish revealed that Chrysichthys maurus hosts the highest diversity of parasitic nematodes, with nine genera identified. Citharinus citharus and Mormyrops anguilloides are each parasitized by only one nematode genus, Cithariniella and Contracaecum, respectively. Except of Spirocamallanus and Camallanus, which were found exclusively in C. maurus, most nematode genera are shared among the different fish hosts. The genus Anisakis exhibits the highest prevalence, with 29.03% in the Senegal River, while Cithariniella shows the highest abundance, mean intensity, and abundance index. Other nematode genera, such as Paracamallanus, Procamallanus, Rhabdochona, Contracaecum, Spirocamallanus, Spinitectus, and Falcaustra, display variable ecological parameters. These nematodes are distributed within the liver and various sections of the digestive tract.
    },
     year = {2025}
    }
    

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  • TY  - JOUR
    T1  - Comparison of Specific Ecological Parameters of Nematodes in Six Common Fish Species from the Senegal River and the Gambia River
    
    AU  - Cheikh Mouhamadou Bamba Seck
    AU  - Ephigénie Ndew Dione
    AU  - Malick Diouf
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    JF  - Ecology and Evolutionary Biology
    JO  - Ecology and Evolutionary Biology
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    PB  - Science Publishing Group
    SN  - 2575-3762
    UR  - https://doi.org/10.11648/j.eeb.20251002.12
    AB  - The Senegal River and the Gambia River share the same sedimentary basin, the same source, and have geographical proximity. This study, conducted over three consecutive years in the Senegal River and the Gambia River, aimed to perform a comparative analysis of the prevalence, abundance, mean intensity, and abundance index of nematodes in six fish species common to both locations: Citharinus citharus, Clarias gariepinus, Chrysichthys maurus, Hydrocynus forskahlii, Mormyrops anguilloides, and Synodontis ocellifer. The inventory of parasitic nematodes in these fish revealed that Chrysichthys maurus hosts the highest diversity of parasitic nematodes, with nine genera identified. Citharinus citharus and Mormyrops anguilloides are each parasitized by only one nematode genus, Cithariniella and Contracaecum, respectively. Except of Spirocamallanus and Camallanus, which were found exclusively in C. maurus, most nematode genera are shared among the different fish hosts. The genus Anisakis exhibits the highest prevalence, with 29.03% in the Senegal River, while Cithariniella shows the highest abundance, mean intensity, and abundance index. Other nematode genera, such as Paracamallanus, Procamallanus, Rhabdochona, Contracaecum, Spirocamallanus, Spinitectus, and Falcaustra, display variable ecological parameters. These nematodes are distributed within the liver and various sections of the digestive tract.
    
    VL  - 10
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