Int. Jr. Bioinformatic and Biological Sci. : v.2 n.3 and 4, p. 135-144. Dec. 2014
DOI No. 10.5958/2321-7111.2014.00011.0
Heterogeneity in habitat use of three threatened
freshwater catfishes (Siluridae: Siluriformes) in five
major tropical rivers of India
Abhishek Kr. Malakar 1 * , Pallavi 1 , Vineet Kr. Dubey 1 , Karan V. Singh 2 ,
Wazir S. Lakra 3 and R. M. Mishra 4
1 National Bureau of Fish Genetic Resources, Canal Ring Road, Lucknow 226002, Uttar
Pradesh, India.
2 National Bureau of Animal Genetic Resources, Makrampur Campus, Karnal-132001,
Haryana, India.
3 Central Institute of Fisheries Education, Versova, Andheri (W), Mumbai 400061, India.
4 Awadhesh Pratap Singh University, Rewa 486003, Madhya Pradesh, India.
*Corresponding author: abhishekmalakar@gmail.com
ABSTRACT
To identify the priority habitats of the threatened catfishes of the genus Ompok
viz. Ompok pabda, O. pabo and O. bimaculatus in India the effects of habitat
variables on the structure of fish assemblage were evaluated from 40 sampling
sites located in Tones, Gomti, Ganga, Bramhaputra and Hoogly Rivers.
Canonical correspondence analyses were carried out to determine the influence of
environmental conditions on species occurrences and assemblage characteristics.
The microhabitat, hydromorphological parameters (depth and current velocity)
followed by conductivity, temperature and total dissolve solid (TDS) were found
to be significant in structuring the assemblage of the three catfishes. Fast water
with shallow depth in different rivers was significantly associated with occurrence
of O. pabda whereas slow water and higher depth were significantly associated
with O. bimaculatus. Some other environmental parameters such as conductivity,
TDS and pH were also found to be significant in shaping the habitat preference of
the Ompok species studied. Our results depicted the importance of environment
influences on the Ompok species which are of conservation and management
interest.
Keywords: Ompok species, Habitat, Aquatic Biodiversity, Riverine System
Freshwater ecosystems have frequently been cited as the most altered and
threatened habitats by human activities (Dudgeon, 1992). Disturbance to physical
habitat and water quality have resulted in fish assemblage shifts, decreased native
species diversity, community homogenization, range reduction and extinction
(Gorman and Karr, 1978; Rabeni and Smale, 1995; Jones et al., 1999; Marchetti