DNA Barcoding and Phylogenetics of Wallago attu Using Mitochondrial COI Gene from the River Indus Abstract Objectives: DNA barcoding technique for fish identification is an effective, rapid, and precise method as compared to the morphological method.
Cytochrome c oxidase subunit 1 gene
-based
DNA barcoding
is frequently used in species identification and biodiversity studies. The
current study was
designed
to identify the fishes
with
the
help of
DNA barcoding
method
resulting
COI gene
sequences
, which were used in the construction of genetic diversity and evolutionary history of Wallago attu inhabiting different sites of the River Indus. Methods: The short mDNA gene sequence of 650 base pairs (COI) was amplified, sequenced, and analyzed by using different bioinformatics tools. The Pairwise distance and
phylogenetic analysis
by
Maximum Likelihood
(ML)
tree based on Kimura
2
Parameter
method was constructed by using MEGA 11 software. Results: Pairwise genetic distance among species showed less divergence between a minimum of 0.000% and a maximum of 0.038%. The Percentage base composition of sequenced samples was calculated and overall AT content (53.7%) was found higher in all sequences as compared to GC content (46.2%). The Phylogenetic tree revealed that species clustered differently under diverse nodes. It revealed that fish species clustered together because they were in the same order and family. QR code in this study was first time developed to guide misleading and fraud cases. Conclusions: These results showed that fish species share identical genera but with diverse genetic variations due to diverse habitats involving a common ancestor. The COI barcodes generated in the current study will help in species identification. Key words: Wallago attu; Morphological Identification; COI Gene; DNA Barcoding; Phylogenetic Analysis 1. Introduction In Pakistan,
the number of
freshwater
fish species is
not
more than
193 (Abro et al., 2020). In River Indus Pakistan, more than 180 freshwater fish species have been recorded (Sheikh et al., 2017). In its tributaries, a high range of diverse, commercially important and representative fish fauna has been found annually. Many scientists have huge data on the diversity and distribution pattern of fish but they still, need a lot of attention (Hussain et al., 2016). Pakistan has varied water resources comprising dams, rivers, streams, and canals.
The River Indus
system
is the largest river
system in
Pakistan
. Near Kailas Mount, River Indus originates in the Tibet Gangdise Range. The Chenab, Sutlej, Jhelum, and Ravi also drain into River Indus in the Punjab plains (Mirza and Mirza, 2014). It had a diverse variety of fish species. Almost 43 native fish species are economically and commercially important (Sherzada et al., 2020). Among all these species, Wallago attu is important economic fish belonging to the family Siluridae under the order Siluriforms. Malee is a common name for W. attu with Vulnerable conservation status (Ng et al., 2019). W. attu is widely distributed in Asian countries, including Pakistan, Nepal, India, Bangladesh, Indonesia, Vietnam, Sri Lanka, and Afghanistan (Siraj et al., 2016). It is a catfish with a fast growth rate and a good food fish with high nutritional value (Gupta, 2015). It has high protein content. Due to its importance and environmental changes, it is near to being threatened (Hussain et al., 2016). According to researchers, there is a need to improve conservation and its protection. The study of the morphology of fishes
plays a vital role in the
betterment
of
conservation, evolution, ecology,
and
environmental variations (Ozcan and Altun, 2015). Morphological relationships play an important role between fish stock identification and species population and distribution. But
it is difficult to identify
this
species
exactly
based on
morphology due to the lack of some morphological features and also taxonomic expertise. DNA barcoding can offer a precise and rapid method of identification of Wallago attu (Bhattacharjee et al., 2012).
DNA barcoding is the most commonly used
genetic technique
for species identification and has
also
been used
for
species
discovery in different organism groups (Ude
et al., 2020
; Kamran
et al
., 2020; Tsoupas
et al
., 2022). DNA barcoding
method in
which a small mitochondrial gene fragment was used for species identification was developed by
Hebert and his colleagues at the
University
of
Guelph in
Canada
(Rahman et al., 2019). In this method, small fragments of mitochondrial gene almost 655bp of COI gene fragment from the 5′ were
used as a
standard
marker for the identification of
eukaryotic
species
including vertebrates and invertebrates (Keskİn and Atar, 2013). Due to the advancement in computational techniques, DNA sequencing becomes the major source to understand genetics and evolutionary relationships (Hajibabaei et al., 2007). DNA barcode system is applicable for all fish species identification and is a simple, reliable, accurate, and cheap method
for the identification of species (Lakra et al., 2011
; Becker
et al
., 2011). A good barcode has less intraspecific distance than interspecific (Hajibabaei
et al
., 2007).
DNA barcoding can
accurately differentiate between
the
species which have highly similar morphological features. This method can identify species at any developmental stage. Cryptic species can also be identified using this technology (Bingpeng et al., 2018). For the discrimination
between closely
resembled
species across
dissimilar
animal phyla
mitochondrial Cytochrome c oxidase subunit I
is best
for
molecular analysis of
marine and
freshwater fishes (Hebert et al., 2003). For differentiation of a vast variety of animal species presently, there is no such great data on W. attu ecology, biology, and molecular analysis in the area of the River Indus, Punjab, Pakistan. Keeping
in view the above facts, the study was
planned
to
assess morphology, meristic characteristics, and DNA barcoding of W. attu from the River Indus. The study will be a great addition to the research and conservation of W. attu in the River Indus, Punjab, Pakistan. 2. Materials and methods Ethic statement: All procedures regarding the sampling were according to the protocols of the ethical review committee of Government College University Faisalabad, Pakistan in line with the international standards on animal experimentation. 2.1. Sampling sites
Fish samples were collected with the help of
commercial
fishermen
using small meshed
cast
nets from seven different sites along an 85 Km stretch of the River Indus, Punjab, Pakistan from upstream to downstream viz., Kalabagh (L1), DaudKhel (L2), Mochh (L3), Rokhri (L4), Mianwali (L5), Ghandi (L6) and Chashma (L7). Fish samples of around 500g were collected from these locations (S1-S7). The collected specimens were preserved in absolute ethanol and then transferred
to the research laboratory, Department of Zoology, Government College University Faisalabad
. 2.2. Morphological
analysis
Identification of all morphometric characters was done by using a special key of the fishes of Punjab, Pakistan (Mirza and Sharif, 1996). All morphometric measurements of each sample were done with the help of scales, magnifying glass, and vernier calipers were done at room temperature (Fig. 1). After the identification based on morphology samples were further processed for DNA barcoding. Fig. 1. Wallago attu 2.3. DNA extraction and PCR amplification
A small piece of ethanol preserved tissue
was cut-off
to
isolate
DNA
by using “QIAampR DNA Mini Kit” following the directions of manufacture. A conserved region was amplified from
5/ end of COI gene using the
under given
primers
. The
Cytochrome c oxidase subunit
1 (
COI) gene was amplified
with the help
of universal primers
synthesized from (MACROGEN Inc., Seoul, Korea)
Fish F1 & Fish R1
(Ward
et al
., 2005; Kamran
et al., 2020
). Primer sequences
were: FishF1: (5/ TCAACCAACCACAAAGACATTGGCAC 3/) FishR1: (5/ TAGACTTCTGGGTGGCCAAAGAATCA 3/) The
final volume of
PCR
reaction was 25µl which included 1X reaction buffer, 1µl template DNA, 2.5mMdNTPs, 2.5mM MgCl2, 0.2 U TaqDNA polymerase and 0.5 µl of each primerin PCR machine
DNA Engine Tetrad 2 Peltier Thermal Cycler (BIO-RAD). PCR amplification
conditions were
as follows
:
94ᴼC for
5
min; 94ᴼC for 30 sec
, variable temperature
for
30
sec
, 72ᴼC 40 sec
for
35 cycles; 72ᴼC for 7 minutes.
PCR products were
envisioned
on 1% agarose gel electrophoresis
tainted
with ethidium bromide
. 2.4. PCR product purification and standard sequencing The polymerase chain reaction sequencing was performed using Genetic Analyzer (
ABI PRISM 3730XL Analyzer 96 capillary type
). Cycle
sequencing was
passed out by
using the Big Dye
(R
Terminator v3.1) Cycle Sequencing Kit (Applied Biosystems
). 3. Statistical and sequence analysis Morphological parameters were analyzed using Minitab 17 software by one-way ANOVA and t-test. The sequencing data were converted into FASTA format. BLASTS of the COI sequences were done at the NCBI to determine the best match homology. Evolutionary analysis of the aligned sequences was conducted in the software MEGA 11. The phylogenetic tree was rooted using Ompok bimaculatus as an out group. The history of evolution was directed using the Maximum Likelihood method (Nei and Kumar, 2000). Evolutionary divergence was
calculated using the Kimura 2-parameter distance model (Kimura, 1980
). Sequenced data was used to generate unique QR code by using an online QR code generator for precise detection of this specie. 4. Results The species were first identified by shape, size, fin ray count, color, and other morphometric and meristic characteristics (Table 1). All these characters showed significant differences (p<0.005) between and within groups. Pectoral fins of fish belonging to the family Siluridae, genus wallago were considered for DNA barcode creation. Amplification of the mitochondrial COI gene of 650 bp was done by using Fish F1 and Fish R1 primers. There were 605 of 675 conserved sites, 61 of 675 variable sites, 33 of 675 parismony informative sites, and 28 of 675 singleton variable sites found in the barcodes. Transversional substitutions (sv = 71.36) were found to be more common than transitional substitutions (si = 28.65), with R ratio of 0.40 for the dataset. BLAST analysis revealed that all the sequences of COI gene of W. attu specimens have a similarity (100%) with the respective sequence in the mitochondrial region in the GenBank database (Table 2).
After editing the consensus length of all barcode sequences was 655 bp and no
deletions, insertions, or
stop codons were observed in any
sequence. All analyzed
sequences were
more
than 600 bp
which confirmed that NUMT (Nuclear DNA sequence originated from mDNA
sequences and are less than
600bp
in length) were not sequenced in
the present study. Table 1 Mean (±SD) morphometric characters of Wallago attu from different sites of the River Indus. Morphometric characters Locations (
mm) L1 L2 L3 L4 L5 L6 L7
( Kalabagh) (DaudKhel) (Mochh) (Rokhri) (Mianwali) (Ghandi) (Chashma) TL 318.99±11.70 295.38±46.47 322.29±23.93 308.38±39.88 273.81±25.37 281.42±29.68 273.59±38.05 SL 254.35±55.74 258.20±39.75 265.27±42.77 261.25±42.99 248.52±27.45 235.27±19.38 220.56±4.64 FL 289.65±31.58 270.44±53.45 295.83±33.07 298.85±28.89 260.42±33.32 258.63±26.70 240.54±30.44 HL 55.51±4.14 57.71±6.27 60.48±4.53 58.13±5.88 52.76±3.05 54.24±4.32 53.54±5.79 SnL 24.20±3.53 25.52±0.94 26.73±1.79 25.37±1.48 24.94±1.25 26.30±2.05 25.94±3.34 ED 7.08±1.16 7.52±0.14 8.18±0.53 7.61±0.54 7.08±1.10 7.50±1.17 7.16±1.60 PrDL 75.79±7.61 76.00±8.51 80.19±5.17 78.97±5.72 72.22±5.07 73.47±4.82 70.85±6.76 PsDL 185.30±34.92 177.36±39.90 198.08±22.36 196.44±23.20 171.10±18.78 172.75±18.70 162.24±21.34 Table 2 Accession No. and BLAST results of Wallago attu. Query sequence ID Accession No. Query Length Percent Identity E- Accession Query value No. of the Cover best match W. attu(L1) W. attu(L2) W. attu(L3) W. attu(L4) W. attu(L5) W. attu(L6) W. attu(L7) W. attu(L1) W. attu(L1) W. attu(L2) W. attu(L2) W. attu(L3) W. attu(L3) W. attu(L4) W. attu(L4) W. attu(L5) W. attu(L5) W. attu(L6) W. attu(L6) W. attu(L7) W. attu(L7) MZ461934 MZ461935 MZ895367 MZ895368 MZ895369 MZ913725 MZ913726 OP482183 OP482270 OP482296 OP520920 OP520921 OP520930 OP520931 OP521220 OP521572 OP521769 OP521770 OP524192 OP563463 OP566851 633 99.68% 595 100% 619 100% 605 100% 623 100% 621 100% 623 100% 644 97.57% 618 99.84% 605 99.67% 631 100% 616 99.84% 618 99.19% 616 96.91% 616 99.02% 629 98.25% 629 98.09% 628 98.41% 616 99.84% 644 100% 659 100% 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 MK572628.1 100% JX983507.1 100% MZ312383.1 100% MN368903.1 100% JX983507.1 100% FJ170767.1 99% MK572628.1 100% MN368898.1 98% MN368898.1 99% MN368903.1 99% MN368898.1 100% MN368898.1 100% MN368902.1 100% MN368898.1 100% MN368902.1 100% MN368897.1 100% MN368897.1 100% MN368895.1 100% MN368898.1 100% MW150846.1 100% MW150844.1 100% A Phylogenetic
tree was constructed by using the maximum likelihood
(ML)
method based on the
K2P method (Fig.
2
). The analysis involved 21 nucleotide sequences of experimental species. To compare with experimental specie some reference sequences from 6 NCBI
with accession numbers from the BLAST search were downloaded
to minimize error for identification. After this, experimental and reference sequences were arranged in FASTA format. Then, all sequences were uploaded to MEGA 11 software for advance alignment, construction and analysis, of the phylogenetic tree. The analysis concerned 39 consensus sequences. Positions of codon were included
1st+2nd+3rd+Noncoding. Gaps and missing data
from all sequences
were eliminated
. After elimination of all gaps total 572 positions were remained in the final sheet. By using MEGA 11 software all evolutionary analyses were accomplished. The evolutionary tree between specie exposed that the majority of the specie clustered simultaneously indicating less divergence between them. Similarly, these species showed less pairwise genetic distance (Table 3). The Percentage base composition of all 4 bases in COI sequences of all W. attu from seven sites was calculated (Table 4).
The overall mean nucleotide base frequencies observed for these sequences were T
(28.6%),
C
(27.9%),
A
(25.1%),
and G (18
.3%).
The
overall
AT content (53
.7%)
was higher than GC content (46
.2%). This is
the
first study of this specie from the selected sites to generate QR codes for accurate identification of W. attu. This specie could be identified with their unique QR code (Fig. 3). Fig. 2. Maximum likelihood tree representing genetic relationship among Wallago attu. 8 Table 3 Pairwise distance using K2P in COI gene 1. MZ461934 L1 2. MZ461935 L2 3. MZ895367 L3 4. MZ895368 L4 5. MZ895369 L5 6. MZ913725 L6 7. MZ913726 L7 8. OP482183 L1 9. OP482270 L1 10. OP482296 L2 11. OP520920 L2 12. OP520921 L3 13. OP520930 L3 14. OP520931 L4 15. OP521220 L4 16. OP521572 L5 17. OP521769 L5 18. OP521770 L6 19. OP524192 L6 20. OP563463 L7 21. OP566851 L7 1 2 0.004 0 0.004 0 0.004 0.004 0 0 0.004 0 0.004 0.005 0.009 0.002 0.005 0.004 0.007 0 0.004 0 0.005 0.002 0.007 0.007 0.036 0.032 0.011 0.014 0.014 0.018 0.016 0.019 0.016 0.002 0.005 0.004 0 0.004 0 3 0 0.004 0 0 0.005 0.002 0.004 0 0.002 0.007 0.032 0.014 0.018 0.019 0.019 0.002 0.004 0.004 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 0.004 0 0 0.005 0.002 0.004 0 0.002 0.007 0.032 0.014 0.018 0.019 0.019 0.002 0.004 0.004 0.004 0.004 0 0.009 0.005 0.005 0.005 0.002 0.002 0.007 0.007 0.004 0.004 0.009 0.005 0.004 0 0 0.005 0.002 0.004 0.005 0.002 0.002 0.007 0.004 0.002 0.002 0.007 0.007 0.007 0.012 0.009 0.011 0.007 0.009 0.036 0.032 0.032 0.038 0.034 0.036 0.032 0.034 0.032 0.011 0.014 0.014 0.019 0.012 0.018 0.014 0.016 0.011 0.032 0.014 0.018 0.018 0.023 0.019 0.018 0.018 0.019 0.014 0.029 0.011 0.016 0.019 0.019 0.025 0.021 0.023 0.019 0.021 0.023 0.038 0.027 0.027 0.016 0.019 0.019 0.025 0.021 0.019 0.019 0.018 0.016 0.03 0.019 0.023 0.029 0.005 0.002 0.002 0.007 0.004 0.002 0.002 0 0.009 0.034 0.016 0.019 0.021 0.018 0 0.004 0.004 0.009 0.005 0.007 0.004 0.005 0.007 0.036 0.011 0.014 0.016 0.016 0.005 0 0.004 0.004 0.009 0.005 0.007 0.004 0.005 0.007 0.036 0.011 0.014 0.016 0.016 0.005 0 9 Table 4
Base composition (%) of all samples of
Wallago attu
from
the
River
Indus. Accession No. MZ461934 L1 MZ461935 L2 MZ895367 L3 MZ895368 L4 MZ895369 L5 MZ913725 L6 MZ913726 L7 OP482183 L1 OP482270 L1 OP482296 L2 OP520920 L2 OP520921 L3 OP520930 L3 OP520931 L4 OP521220 L4 OP521572 L5 OP521769 L5 OP521770 L6 OP524192 L6 OP563463 L7 OP566851 L7 Avg. T 28.8 29.0 28.3 28.5 28.6 28.2 28.5 29.2 28.5 28.6 28.7 28.6 28.4 28.0 28.8 28.7 28.5 28.7 28.6 28.9 29.3 28.6 C A 27.1 25.2 27.4 25.1 27.3 25.4 27.5 25.5 27.2 25.1 27.3 25.3 27.2 25.2 27.5 25.5 28.4 25.3 28.0 25.3 28.4 25.1 28.3 25.2 28.2 25.4 28.3 25.5 28.3 25.2 28.5 24.8 28.8 24.7 28.5 24.4 28.3 25.2 27.5 24.9 27.2 24.8 27.9 25.1 G 19.0 18.5 18.9 18.5 19.1 19.2 19.1 17.7 17.8 18.0 17.8 17.9 18.0 18.2 17.7 18.0 18.0 18.3 17.9 18.7 18.7 18.3 Total 632.0 594.0 618.0 604.0 622.0 620.0 622.0 643.0 617.0 604.0 630.0 615.0 617.0 615.0 615.0 628.0 628.0 627.0 615.0 643.0 658.0 622.2 GC% 46.1 45.9 46.2 46 46.3 46.5 46.3 45.2 46.2 46 46.2 46.2 46.2 46.5 46 46.5 46.8 46.8 46.2 46.2 45.9 46.2 AT% 54 54.1 53.7 54 53.7 53.5 54.7 54.7 53.8 53.9 53.8 53.8 53.8 53.5 54 53.5 53.2 53.1 53.8 53.8 54.1 53.7 Wallago attu Fig. 3. QR codes generated using Fasta Sequences of Wallago attu 5. Discussion It is very important to identify fish biodiversity accurately before the utilization of fish in any field. The standard and traditional approach for fish identification is based on morphological characters, but when there is phenotypic plasticity this approach is not reliable. To understand the speciation and phylogenetic relationship of fishes in the past, the only tools were meristic and morphometric. By the investigation of
a small fragment of the
whole
genome, the
discrimination
of
biodiversity is allowed by the micro genomic identification system. Mitochondrial DNA of animals is the best technology
for the identification of species
analysis than nuclear
DNA
due to the lack of haploid and introns approach of inheritance. (
Cytochrome c oxidase subunit I
) COI
gene
is
used as
a standard marker
for the bio-identification of species (Hebert et al
., 2003). In the current study, thirty-five (35) individuals of Wallago attu (catfish: Siluridae family) were collected from River Indus Punjab, Pakistan. 21 out of 35 samples were processed for DNA barcoding. These samples were initially identified based on morphological characters and to resolve the taxonomic problems; a molecular study has also been done considering
the effectiveness of DNA barcoding for the identification of
W. attu. Therefore, this study shows so as to the results obtained from the morphometric and molecular analysis is similar. W. attu is rare and ranked near threatened (Khan et al., 2008) in this area due to which a limited number of samples were taken for this study. Identification based on morphology is a basic method to know about demographic characteristics, growth, and systematic variation of fish. Morphometric analysis performs a vital
role in the estimation of the relationship between different body parts
. The Mean and standard deviation of all the samples showed that all relationships of TL with HL, SL, SnL, FL, ED, PrDL, and PoDL are extremely significant (p<0.005), showed that all (length-length relationships) LLRs are considerably interrelated (Table 1, 2). These extremely significant relationships in the current study for length-length relationships are in universal harmony
with other studies
described
on
Tor potitura (
Naeem et al
., 2011b), Oreochromis mossambicus (
Naeem et al
., 2011a). The morphological parameters demonstrated a comparative constructive
increase with an increase in the length of fish. (Ujjania et al., 2012
) too revealed that with an enhancement in fish length morphometric parameters were also recorded with positive growth. Meristic counts were almost invariable with different body lengths in all the collected samples of fish,
so it
concluded
that the meristic counts were independent of body length
(Ishtiaq et al., 2016). 11 5.1. DNA barcoding At species level identification, an effective and advanced method is DNA barcoding. The Barcoding technique can be applied all over the samples. It can be used for fresh as well as preserved samples (Cawthorn et al., 2012). The Mitochondrial COI gene with 655 base pairs is considered a universal barcode for animals due to its high number of exons, fast mutation rate, and high availability all over the cells and maternal inheritance. DNA barcoding gives accurate identification of taxon and also covers the issues of conservation in biodiversity. Genetic sequences obtained from the species assemblage are uploaded to the barcode library. In recent years, barcoding
of freshwater fishes has
particularly donated to
the global GenBank
dataset
from
diverse reservoirs,
lakes, and
riverside systems (Kundu et al., 2019). Superlatively, interaspecific divergence should be about 10 times less than interspecific divergence (Hebert et al., 2004).
Clear sequence divergence between species
that is
coupled with sequence conservation within species confirmed the barcode COI sequence as highly
specific
and
variable. 5.2. Phylogenetic tree analysis Phylogenetic tree analysis showed identical categorization regarding morphology and taxonomy beside with non-significant differentiation at
taxonomic levels. Our
findings showed
the
worth
of barcoding for the
exact
identification and
authentification
of
freshwater
fish
species of the River Indus. In this study, 21 freshwater fish samples of W. attu were categorized. Within species together branch length is more bunched
than the branch length between species which are deeper. This confirms the
finding
of (Meyer
and Paulay, 2005) branch length
tends to be much deeper between
species than between
conspecific individuals
. The phylogenetic tree noticeably separates the Wallago attu samples on the bases of
genetic distance. (Ward et al
., 2005)
in their
Australian fish species
study
verified effectiveness
of
phylogenetic tree in distinctive species through presenting fourteen diverse clusters from fourteen flathead species. The evolutionary analysis was summarized with the help of
Maximum Likelihood method
(ML)
based on the
K2P
model. The
analysis involved 21 nucleotide sequencing of W. attu. All gaps and missing data were removed and evolutionary examination was accomplished in MEGA 11 software (Karim et al., 2018). The study of tilapia renowned dissimilar tilapia fish species into diverse clustered groups (Sogbesan et al., 2017). These results demonstrated that all individuals of a species collected together. In the phylogenetic tree, W. attu MZ913726, OP520920 and MZ913725 originated from same cluster showed these are sister species, while W. attu MN49555.1 is more closely related to the above-mentioned species (Fig. 1). In this tree, all sequenced samples are closely related to each other and showed less divergence because all these species belong to the same genus. Phylogenetic clade showed more divergence between Wallago attu and Ompok bimaculatus due to having different genera. 5.3. Pairwise genetic Distance (K2P) In our investigations, K2P model was utilized to estimate pairwise genetic difference between species. The average distance among species was a minimum of 0.000% and a maximum of 0.038% because distance decreases as we move from family to species level (Table 4). As we studied about single specie our results showed the less genetic difference. Our findings are reliable with the earlier study by (Mudumala et al., 2011). 5.4. Nucleotide base Discrimination The Percentage base composition of all four bases in partial COI sequencing of all W. attu samples from the River Indus was collected (Table 4). Our results demonstrated that the composition of average nucleotide bases was 46.2% GC and 53.7% AT catfish. The average GC content was less than the average AT content. Overall excessive thymine nucleotide as compared to other nucleotide bases was found in all sequences, this outline
is also
examined
in other cyprinid species as
pragmatic
by (Meyer
and Paulay,
2005
; Karim et al., 2018). 5.5. DNA sequence based generated QR codes This is barcode base study due to which we generated QR codes that be capable of scan by using cell phone application. This method is similar as barcodes scanned in superstore (Fig. 4). In this study, we generated QR code for the 1st time based on the molecular level for the identification of freshwater catfish Wallago attu. QR code of this specie was generated and named.
Yang et al. (2019
) generated 1st time
DNA sequence based QR
code which differs from our approach. As there is no previous DNA-based study for Wallago attu fish collected from River Indus, Pakistan. As
the results of the present study, provide
early
data
for possible mitochondrial genomes and some phylogenetic research. It is necessary to understand further DNA research studies on commercially important catfish Wallago attu of family Siluridae from the River Indus are requisite, as understanding between catfish obtainable genetic resources could prove helpful for scheming future genetic breeding programs. 6. Conclusions In the current study, the identification of catfish Wallago attu was done based on morphology which was further confirmed through DNA barcoding. Morphological identification has many limitations due to which DNA barcoding has enough variability to differentiate among species. This research will be helpful for future researchers and this data has a great addition to River Indus biodiversity and conservation.
Declaration of Competing Interest The authors
declared
that they have no known competing
financial interest
or personal relationships that could have appeared to influence the work reported in this paper. Acknowledgements The authors are grateful to
Higher Education Commission
of
Pakistan
for funding this
research project under grant number 5698/PUNJAB/
NRPU/R&D/HEC
/2016
and the Punjab
Fisheries Department for helping sample collection. References 1. Abro, A.N., Waryani, B., Narejo, T.N., Ferrando, S., Abro, A.S., Abbasi, R.A., Ul- Hassan, H., 2020. Diversity of freshwater fish in the lower reach of Indus River, Sindh province section, Pakistan. Egypt. J. Aquat. Biol. Fish, 24(6), 243-265. https://dx.doi.org/10.21608/ejabf.2020.111114. 2. Becker, S., Hanner, R., Steinke, D., 2011. Five years of FISH-BOL: Brief status report. Mit. DNA, 22(sup1), 3-9. https://doi.org/10.3109/19401736.2010.535528. 3. Bhattacharjee, M.J., Laskar, B.A., Dhar, B., Ghosh, S.K., 2012. Identification and re- evaluation of freshwater catfishes through DNA barcoding. PloS one, 7(11), e49950. https://doi.org/10.1371/journal.pone.0049950. 4. Bingpeng, X., Heshan, L., Zhilan, Z., Chunguang, W., Yanguo, W., Jianjun, W., 2018. DNA barcoding for identification of fish species in the Taiwan Strait. PloS One, 13(6), e0198109. https://doi.org/10.1371/journal.pone.0198109. 5. Cawthorn, D.M., Steinman, H.A., Witthuhn, R.C., 2012. DNA barcoding reveals a high incidence of fish species misrepresentation and substitution on the South African market. Food Res. Int. 46 (1), 30-40. https://doi.org/10.1016/j.foodres.2011.11.011. 6. Gupta, S., 2015. Wallago attu (Bloch and Schneider, 1801), a threatened catfish of Indian waters. Int. J. Res. Fish. Aquac. 5(4), 140-142. http://www.urpjournals.com/. 7. Hajibabaei, M., Singer, G.A., Hebert, P.D., Hickey, D.A., 2007. DNA barcoding: how it complements taxonomy, molecular phylogenetics and population genetics. Trends in Genetics, 23(4), 167-172. https://doi.org/10.1016/j.tig.2007.02.001. 8. Hebert, P.D., Penton, E.H., Burns, J.M., Janzen, D.H., Hallwachs, W., 2004. Ten species in one: DNA barcoding reveals cryptic species in the Neotropical skipper butterfly Astraptes fulgerator. Proceed. Nat. Acad. Sci. 101(41), 14812-14817. https://doi.org/10.1073/pnas.0406166101. 9. Hebert, P.D., Ratnasingham, S., De Waard, J. R., 2003. Barcoding animal life: cytochrome c oxidase subunit 1 divergences among closely related species. Proceedings of the Royal Society of London. Series B: Biological Sciences, 270 (suppl_1), S96-S99. https://doi.org/10.1098/rsbl.2003.0025. 10. Hussain, M.Z., Latif, A., Shahzadah, W.A., Hussain, S., Iqbal, R., Ali, M., 2016. Diversity, abundance and seasonal variations of fish community in lentic water bodies of Indus River at Ghazi Ghat, Pakistan. Pak. J. Zool. 48(1), 59-65. 0030-9923/2016/0001- 0059. 11. Hussain, S., Hussain, M.Z., Iqbal, R., Abbas, K., Mahmood, J.A., Iqbal, F., Ali, M., 2016. Diversity and status of Ichthyofauna of hill torrents of Suleman Mountain Range, Dera Ghazi Khan region, Pakistan. Pak. J. Agri. Sci. 53(4), 833-842. DOI: 10.21162/PAKJAS/16.4849. 12. Ishtiaq, A., Naeem, M., 2016. Length-weight relationships and condition factor for farmed Catla catla (Hamilton, 1822) from Southern Punjab, Pakistan. Punj. Univ. J. Zool. 31(2), 209-214. 97-PUJZ-61022270/16/0209-0214. 13. Kamran, M., Yaqub, A., Malkani, N., Anjum, K.M., Awan, M.N., Paknejad, H., 2020. Identification and Phylogenetic Analysis of Channa Species from Riverine System of Pakistan Using COI Gene as a DNA Barcoding Marker. J. Bioresou. Manag. 7(2), 10. https://doi.org/10.35691/JBM.0202.0135. 14. Karim, A., Saif, R., Ali, F.S., Gil, Z., & Ali, W., 2018. Use of CO1 gene sequences for computing genetic diversity between Cirrhinusmrigala from two different habitats (Farm and River). In Basic & Clinical Pharmacol.Toxicol. 3(2), 54-57. 15. Keskİn, E., Atar, H.H., 2013. DNA barcoding commercially important fish species of Turkey. Mol. Ecol.Resour. 13(5), 788-797. https://doi.org/10.1111/1755-0998.12120. 16. Khan, A.M., Shakir, H.A., Khan, M.N., Abid, M., Mirza, M.R., 2008. Ichthyofaunal survey of some freshwater reservoirs in Punjab. J.A.P.S. 18(4), 151-154. 17. Kimura M., 1980. A simple method for estimating evolutionary rate of base substitutions through comparative studies of nucleotide sequences. J. Mol. Evo. 6(111-120). 18. Kundu, S., Chandra, K., Tyagi, K., Pakrashi, A., Kumar, V., 2019. DNA barcoding of freshwater fishes from Brahmaputra River in Eastern Himalaya biodiversity hotspot. Mit. DNA Part B, 4(2), 2411-2419. https://doi.org/10.1080/23802359.2019.1637290. 19. Lakra, W.S., Verma, M.S., Goswami, M., Lal, K.K., Mohindra, V., Punia, P., Hebert, P., 2011. DNA barcoding Indian marine fishes. Mol. Ecol. Resour. 11(1), 60-71. https://doi.org/10.1111/j.1755-0998.2010.02894.x. 20. Meyer, C.P., Paulay, G., 2005. DNA barcoding: error rates based on comprehensive sampling. PLoS Biol. 3(12), e422. https://doi.org/10.1371/journal.pbio.0030422. 21. Mirza, M.R., Mirza, Z.S., 2014. Longitudinal Zonation in the Fish Fauna of the Indus River in Pakistan. Biologia, 60(1), 149-152. 22. Mirza, M.R., Sharif, H.M. 1996. A Key to fishes of the Punjab, Ilmi Kitab Khana, Lahore, Pakistan. 23. Mudumala, V.K., Somvanshi, V.S., Lakra, W.S., 2011. Phylogenetic relationships of coastal tunas inferred from mitochondrial DNA sequences in the cytochrome c oxidase I (COI) gene—a study on DNA barcoding. November. In First meeting of the IOTC Working Party on Neritic Tunas, Chennai, India (pp. 14-16). 24. Naeem, M., Salam, A., Baby, R., Ali, M., Ishtiaq, A., Ashraf, M., 2011a. Length–Weight relationship of female population of farmed Oreochromis mossambicus in relation to body size and condition factor from Pakistan. International Conference on Bioscience, Biochemistry and Bioinformatics, IPCBEE Vol. 5 pp. 360-363. IACSIT Press, Singapore 25. Naeem, M., Salam, A., Ashraf, M., Khalid, M., Ishtiaq, A., 2011b. External morphometric study of hatchery reared mahseer (Tor putitora) in relation to body size and condition factor. Afr. J. Biotech. 10(36), 7071-7077. DOI: 10.5897/AJB11.715. 26. Nei, M., Kumar, S., 2000. Molecular evolution and Phylogenetics. Oxford University Press. 27. Ng, H.H., de-Alwis-Goonatilake, S., Fernado, M., Kotagama, O., 2019. Wallago attu (errata version published in 2020). The IUCN Red List of Threatened Species, e.T166468A174784999. 28. Ozcan, G., Altun, A., 2015. Length-weight relationship and condition factor of three endemic and threatened freshwater fishes from Orontes River. Pak. J. Zool. 47(6), 1637- 1643. 0030-9923/2015/0006-1637. 29. Rahman, M.M., Noren, M., Mollah, A.R., Kullander, S.O., 2019. Building a DNA barcode library for the freshwater fishes of Bangladesh. Sci. reports, 9(1), 1-10. https://doi.org/10.1038/s41598-019-45379-6. 30. Siraj, M., Khisroon, M., Khan, A., 2016. Bioaccumulation of heavy metals in different organs of Wallago attu from River Kabul Khyber Pakhtunkhwa, Pakistan. Biological trace element research, 172(1), 242-250. DOI 10.1007/s12011-015-0572-4. 31. Sheikh, M., Laghari, M.Y., Lashari, P.K., Khooharo, A.R., Narejo, N.T., 2017. Current Status of Three Major Carps (Labeo rohita, Cirrhinus mrigala and Catla catla) In the Downstream Indus River, Sindh. Fish. Aqua. J. 8, 222. DOI: 10.4172/2150- 3508.1000222. 32. Sherzada, S., Khan, M.N., Babar, M.E., Idrees, M., Wajid, A., Sharif, M.N., Shahid, M., 2020. Identification of three cyprinidae family members through cytochrome oxidaseI. Pakistan J. Zool. 52(1), 1-4. https://dx.doi.org/10.17582/journal.pjz/2020.52.1.sc13. 33. Sogbesan, O.A., Sanda, M.K., Jaafar, J.N., Adedeji, H.A., 2017. DNA barcoding of tilapia species (Pisces: Cichlidae) from North-Eastern Nigeria. J. Biotec. Biomat. 7(4), 1- 4. DOI: 10.4172/2155-952X.1000277. 34. Tsoupas, A., Papavasileiou, S., Minoudi, S., Gkagkavouzis, K., Petriki, O., Bobori, D., Triantafyllidis, A., 2022. DNA barcoding identification of Greek freshwater fishes. Plos one, 17(1), e0263118. https://doi.org/10.1371/journal.pone.0263118. 35. Ude, G.N., Igwe, D.O., Brown, C., Jackson, M., Bangura, A., Ozokonkwo-Alor, O., Das, A., 2020. DNA barcoding for identification of fish species from freshwater in Enugu and Anambra States of Nigeria. Conservation Genetics Resources, 12(4), 643-658. https://doi.org/10.1007/s12686-020-01155-7. 36. Ujjania, N.C., Kumar, G., Langar, R.K., Krishna, G., 2012. Biometric studies of mahseer (Tor tor. Ham. 1822) from Bari talab (Udaipur), India. Int. J. Innov. Bio-Sci. 2(3), 38– 141. 37. Ward, R.D., Zemlak, T.S., Innes, B.H., Last, P.R., 2005. DNA barcoding Australia's fish species. Philos. Trans. Royal Society Lond. Ser.B, Biol.Sci., 360, 1847-1857. https://doi.org/10.1098/rstb.2005.1716. 38. Yang, C.H., Wu, K.C., Chuang, L.Y., Chang, H.W., 2019. Decision theory-based COI- SNP tagging approach for 126 scombriformes species tagging. Frontiers in Genetics, 10, 259. https://doi.org/10.3389/fgene.2019.00259. 1 2 3 4 5 7 10 12 13 14 15 16 17