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 |
Fish, Nematodes, Prevalence, Abundance, Mean Intensity, Abundance Index
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 |
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 |
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 |
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 |
P | Prevalence |
A | Abundance |
MI | Mean Intensity |
DI | Dominance Index |
S | Senegal River |
G | Gambia River |
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APA Style
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
ACS Style
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
@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} }
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 Y1 - 2025/06/30 PY - 2025 N1 - https://doi.org/10.11648/j.eeb.20251002.12 DO - 10.11648/j.eeb.20251002.12 T2 - Ecology and Evolutionary Biology JF - Ecology and Evolutionary Biology JO - Ecology and Evolutionary Biology SP - 104 EP - 114 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 IS - 2 ER -