Total 30 species of fishes were recorded from Harike wetland and these belong to 14 families and 21 genera. Maximum number of species (12) recorded under family Cyprinidae followed by Bagridae (3 species), Siluridae (3 species), Channidae (2 species), Mastacembelidae (2 species each), Notopteridae (2 species), Schilbeidae (1 species), Sisoridae (1 species), Ambassidae (1species), Belontiidae (1 species each), Clupeidae (1 species), Clariidae (1 species), Synbranchidae (1species), Belonidae (1 species) and Nandidae (1 species each).
Labeo rohita, Cyprinus carpio communis,Catla catla,
Cirrihinus mrigala,
Labeo calbasu of Cyprinidae family;
Rita rita of Bagridae family;
Wallago attu of Siluridae family;
Channa marulius and
C. striatus of Channidae family;
Notopterus notopterus and
N. chitala of Notopteridae family were found in all months. Month wise availability of the fish genera and species depicted in the Table 1. Maximum number of genera (21) and species (30) were recorded in the month of January and minimum number of genera (12) and species (17) were recorded during winters This may be attributed to the onset of winter fish might have migrated towards down- stream of the rivers Two species, most abundantly found in the Harike wetland were
L. rohita and
C. carpio communis of Cyprinidae family in overall catch. In total Cyprinidae family was predominated in catch composition and accounted about 52.53% of total catch composition followed by Siluridae (14.95%), Channidae (10.90%), Bagiridae (7.68%), Notopteridae (7.53%) contributed significantly (Table 2).
Among 250 samples studied for biometric analysis of
L. rohita from Harike wetland average weight (Wt), total length (TL), standard length (SL) and forked length (FL) were recorded 2600±5.64g (1700-3600 g), 58.2±5.65 cm (51.3-67.6cm), 48.0±8.54 cm (42.5-55.5cm) and 46.0±0.25 cm (38.0-54.5cm), respectively. Dorsal fin rays (DFR), Pectoral fin rays (PFR), Anal fin rays (AFR), Caudal fin rays (CFR) ranged from 14-16, 16-18, 5-6 and 18-20, respectively along with Pelvic fin rays (PeFR) recorded 9 in number (Table 3). Biometric study revealed that sufficient numbers of mature
L. rohita are available in wetland to support the recruitment in subsequent years.
L. rohita established negative algometric growth (b= 2.701); thus species became slender as it increased in length (Table 4)
. Choudhury
et al., (1982) reported negative allometric growth (b = 2.347) of
L. rohita from river Brahmaputra, Assam.
Bhat (2011) reported growth coefficient (b) as 2.97 and coefficient of determination (r
2) as 0.98 from Phuj reservoir, Jhansi in
L. rohita. Prasad
et al., (2012) also reported negative allometric growth pattern of
L. rohita from Govindgarh Lake, Rewa. Variation in slope may be attributed due to variation in sample size, life stages and environmental factors
(Kleanthids et al., 1999).
The co-efficient of determination (r
2) values explains the proper fit of the model for growth. In the present study, value of r
2 of
L. rohita was calculated as 0.971 (97% variability) indicating more than 97% variability by the model and good fitness. Condition factor of
L. rohita recorded greater than one (1.16) (Table 4) indicating fish stocks of the wetland maintaining a healthy condition which may be due to availability of preferred food items as evidenced by the present study during gut content analysis study.This values suggest a state of wellbeing for the species tested. Many factors affect the growth condition of fish including reproductive cycles, availability of food, as well as habitat and environmental factors. The deviation of Kn from 1 reveals information concerning the differences in food availability and consequence of physicochemical features on the life cycle of fish species (
Le Cren, 1951).
Genetic diversity in L. rohita
Sequence alignment and phylogenetic analysis
The raw sequencing reads generated by Sanger sequencing were subjected to quality trimming. Sequencing bases from both ends with sequencing Quality Value (QV) of <20 were removed. QV >20 is an established metric for determining the quality of sequencing data. It means that probability of a base being miscalled (wrongly sequenced) was not more than 1%. After quality trimming, the sequencing reads ranged from 497-696 bp in length. Sequence alignment by ClustalW and subsequent phylogenetic tree construction revealed the presence of two distinct clades with majority of COI sequences (14 out of 15) getting clustered in one clade (Fig 1). This particular clade further got diverted into two branches. The phylogenetic tree generated in this study was quite reliable as two outgroup COI sequences belonging to
Sperata seenghala were found to be clustered together and separated from
L. rohita COI sequences.
COI sequence variation in L. rohita
Calculation of intraspecific mean and pairwise distances was performed by MEGA 6.0 software using the K2P parameters. The pairwise distances ranged from 0.00 to 18.49% with a mean±S.E. value of 4.70% ±0.40 (Table 5). During genetic diversity analysis by mitochondrial sequences, numbers of haplotype (h), haplotype div ersity (Hd) and nucleotide diversity (p) are considered as important metrics in any population. A haplotype is a group of genes in an organism that are inherited together from a single parent. Haplotype diversity (also known as gene diversity) represents the probability that two randomly sampled alleles are different, while nucleotide diversity is defined as the average number of nucleotide differences per site in pairwise comparisons among DNA sequences (
de Jong et al., 2011). Being a probability metric, the highest value of haplotype diversity could be one. In the present study, a total of 9 haplotypes were observed in 15
L. rohita COI sequences. The haplotype diversity and nucleotide diversity values were found to be 0.848 and 0.024, respectively. Though no previous data from Harike wetland is available, the genetic diversity of wild populations of
L. rohita in various Indian rivers systems has been investigated by other researchers. In a study by
Luhariya et al., (2012), a total of 35 haplotypes with haplotype diversity of 0.751 and nucleotide diversity of 0.005, were observed in 146 samples of
L. rohita collected from nine distant rivers; Satluj, Brahmaputra, Son, Chambal, Mahanadi, Rapti, Chauka, Bhagirathi and Tons. Comparatively higher (closer to one) value of haplotype diversity in the present study indicated that
L. rohita stocks in Harike wetland were genetically diverse. Moreover, higher nucleotide diversity values in the present study, also indicated more difference between haplotypes in Harike wetland.