Journal of Threatened Taxa |
www.threatenedtaxa.org | 26 July 2021 | 13(8): 19093–19101
ISSN 0974-7907 (Online) | ISSN 0974-7893
(Print)
https://doi.org/10.11609/jott.6281.13.8.19093-19101
#6281 | Received 09 June 2020 | Final
received 08 July 2021 | Finally accepted 10 July 2021
On the freshwater fish fauna of
Krishna River, Sangli District, Maharashtra, India
Suresh M. Kumbar
1 , Shrikant S. Jadhav 2, Swapnali
B. Lad 3, Abhijit B. Ghadage 4,
Satyawan S. Patil 5
& C. Shiva Shankar 6
1,3,4,5 Department of Zoology, Arts,
Commerce and Science College, Vidyanagar, Tal. Palus,
District Sangli, Maharashtra 416310, India.
2,6 Zoological
Survey of India, Freshwater Biology Regional Centre, Inner Ring Road, Attapur, Hyderguda, Hyderabad,
Telangana 500048, India.
1 smkumbar@rediffmail.com
(corresponding author), 2 shrikantjadhavzsi@gmail.com, 3 swapnali5lad@gmail.com,
4 abghadage82@gmail.com, 5 sspatilzoology@gmail.com, 6
cshivashankarchinna@gmail.com
Editor: Rajeev Raghavan, Kerala
University of Fisheries and Ocean Studies (KUFOS), Kochi, India. Date
of publication: 26 July 2021 (online & print)
Citation: Kumbar,
S.M., S.S. Jadhav, S.B. Lad, A.B. Ghadage, S.S. Patil & C.S. Shankar (2021). On the freshwater fish fauna of
Krishna River, Sangli District, Maharashtra, India. Journal of Threatened Taxa 13(8): 19093–19101. https://doi.org/10.11609/jott.6281.13.8.19093-19101
Copyright: © Kumbar
et al. 2021. Creative Commons Attribution
4.0 International License. JoTT allows unrestricted use, reproduction, and
distribution of this article in any medium by providing adequate credit to the
author(s) and the source of publication.
Funding: University Grant Commission,
New Delhi (F. No. 42-619/2013)
Competing interests: The authors
declare no competing interests.
Acknowledgements: We are grateful to the principal,
Arts, Commerce & Science College, Palus, District
Sangli for facilities. We are also thankful to Dr. Kailash Chandra, Director, Zoological Survey of India,
Kolkata; Dr. P.S. Bhatnagar, scientist-E &
officer-in-charge, Western Regional Centre, Zoological Survey of India, Pune
and Dr. Deepa Jaiswal, scientist-E &
officer-in-charge, Freshwater Biology Regional Centre, Zoological Survey of
India, Hyderabad for the facilities and encouragement. The first author thanks
the University Grants Commission, New Delhi, for financial assistance to this
major research project.
Abstract: Freshwater fish fauna of Krishna
River, Sangli district was studied from 2013 to 2017.
A total of 73 species belonging to 10 orders, 22 families, and 49 genera were
recorded, of which, 29 species are endemic to the Western Ghats and 11 species
endemic to the Krishna River system. Labeo kontius, an endemic barb of the Cauvery River System
was recorded for the first time from the Krishna River, Maharashtra. As per the
IUCN Red List of Threatened Species, 54 species are assessed as ‘Least
Concern’, four species as ‘Near Threatened’, three species as ‘Vulnerable’,
five as ‘Endangered’, and two as ‘Data Deficient’. The conservation status of
two species has not yet been assessed. Fish fauna of the Krishna River within
the study area is threatened as a result of alien species, and several
anthropogenic stressors such as pollution from industrial as well as
agricultural sources, human settlements, and overfishing. Since, this small study area harbours 28
endemic and eight threatened species, their conservation should be given high
priority.
Keywords: Conservation, endemic species,
fish diversity, threats, Western Ghats.
The Western Ghats of India is
global biodiversity hotspot (Myers et al. 2000), known for its high level of
endemism of taxonomic groups such as amphibians and freshwater fish. Around 320
species belonging to 11 orders, 35 families, and 112 genera are known from this
region (Dahanukar & Raghavan 2013) and this
number is certain to increase given the high number of species being discovered
on a yearly basis. Krishna is one of the major perennial rivers of the northern
Western Ghats. The river originates at Mahabaleshwar (17.9880N;
73.6370E), Satara District, Maharashtra,
and traverses a distance of 290 km through Satara, Sangli, and Kolhapur districts in Maharashtra, thereafter
flowing through the states of Karnataka and Telangana before emptying into the
Bay of Bengal at Hamasaladeevi in Andhra Pradesh.
Earliest studies on the fish
fauna of Deccan was carried out by Sykes (1839). Specific studies on the fish
fauna of the Krishna River (in addition to the Godavari) were carried out by
David (1963), but no separate ‘river-wise’ locations for the species collected,
were provided. A major study on the fish fauna of Krishna River was also
carried out by Jayaram (1995), but no separate list of fishes collected
specifically from the tributaries in Sangli District
was provided.
Previous studies on the fish
fauna of Krishna River has largely focused on the tributaries in Satara District. Annandale (1919) reported 18 species from
the Yenna River at Medha,
followed by Silas (1953) who studied the fish fauna of Mahabaleshwar and Wai
and recorded 14 species. Arunachalam et al. (2002) recorded 14 species from Dhom reservoir, and subsequently Jadhav et al. (2011) reported
58 species from the Koyna tributary. More recently, Kharat et al. (2012) provided an updated checklist of the
fish fauna of Krishna River at Wai and Dhom
reservoir, and reported the presence of 51 species. The only published work on
the freshwater fishes of the Krishna River in Sangli
District is by Kumbar & Lad (2014) who recorded
13 species of catfishes. In the present paper, we provide a comprehensive
checklist of the freshwater fishes of the Krishna River flowing through Sangli district in Maharashtra and identify possible
threats so as build baseline data for future conservation action.
Methods
Field surveys were undertaken in
the Krishna River, Sangli district, Western
Maharashtra from the year 2013 to 2017. Fish specimens were collected from Bahe (17.1138°N & 74.2811°E), Borgaon
(17.0808°N & 74.3691°E), Sangli (16.8591°N &
74.5577°E), Miraj (16.7877°N & 74.6291°E), and Mhaisal
(16.7358°N & 74.6986°E) (Figure 1), with the help of local fishers using
different mesh-sized gill nets and cast nets. Alternatively, fish samples were
also procured from local fish markets.
Assuming that the fishing effort
for a given type of net was constant, the relative abundance of the fish was
grossly categorized following Dahanukar et al.
(2012), namely abundant (76–100 % of total catch), common (51–75 % of total
catch), moderate (26–50 % of total catch), and rare (1–25 % of total catch).
Samples were preserved in 10% formalin and identified using the available
literature (Menon 1987, 1992; Talwar & Jhingran
1991; Jayaram & Dhas 2000; Jayaram & Sanyal 2003; Jayaram 1991, 2006, 2010) and relevant recent
taxonomic literature related to different groups (Dahanukar
et al. 2011; Keskar et al. 2015; Katawate
et al. 2016; Lavoué et al. 2020; Sudasinghe
et al. 2020). All identified specimens are deposited at the Department of
Zoology, Arts, Commerce and Science College, Palus, Sangli District, Maharashtra, with accession numbers from
ZID 01–73.
Results
We recorded a total 73 species of
freshwater fish belonging to 10 orders, 22 families and 49 genera from the
Krishna River in Sangli district (Table 1). Order Cypriniformes dominated with 42 species, followed by Siluriformes (18 species), Anabantiformes
(three species), Synbranchiformes, Perciformes, & Beloniformes
(two species each), and Cyprinodontiformes, Gobiiformes, Osteoglossiformes,
& Cichliformes (one species each). Representative
species of fish collected from Krishna River are shown in (Images 1, 2, 3 &
4). As per the IUCN Red List of Threatened Species, 54 species are assessed as
‘Least Concern’, four species as ‘Near Threatened’, three species as
‘Vulnerable’, five as ‘Endangered’, two as ‘Data Deficient’, and the
conservation status of two species has not yet been assessed. Of the 73
species, 29 are endemic to the Western Ghats, and 11 are endemic to the Krishna
River System (Table 1). Microlevel distribution of species along the
upstream-downstream gradient showed that 56 species occurred in upper reaches,
28 species in middle stream, and 37 species in downstream respectively (Figure
1). Of the total fish collected, 15 species were found to be common, six
abundant, 28 moderate and 24 rare.
Fish fauna of Krishna River is
severely threatened by pollution from organic wastes particularly around the
towns of Sangli and Miraj as well as from pollution
due to agricultural runoff and sewage. Recently, sand mining has also increased
significantly along the stretch of the river near Bahe
and Borgaon, resulting in the loss of available
habitats to the fish fauna of these areas. Similarly, overfishing,
indiscriminate use of poison to collect fish in large numbers and using
fine-meshed gill-nets, is a specific threat to species of the genera Bangana, Tor, Hypselobarbus,
Labeo, Cirrhinus, Opsarius, Salmostoma, Botia, Mystus, Cirrhinus, and Puntius.
We also recorded seven non-native
species—four transplanted: Cirrhinus mrigala, Labeo rohita, Labeo catla,
Labeo calbasu in all
sites and three alien invasive species: Oreochromis mossambicus,
Cyprinus carpio and Clarias gariepinus at
Sangli and Miraj. Studies in their entirety of
Krishna River by Jayaram (1995) have recorded 10 invasive alien species, but
interestingly Jadhav et al. (2011) could not record any alien species from Koyna tributary. However, Dahanukar
et al. (2012) recoded seven introduced species from Indrayani
River near Pune, and four species from Hiranyekeshi
River by Kumkar et al. (2017).
Discussion
Krishna River harbours a number
of endemic and threatened species. We collected Glyptothorax
cf. poonaensis from Bahe
near Islampur in moderate numbers. These specimens
resemble G. poonaensis (Hora 1938), but
differs considerably with the description provided in Dahanukar
et al. (2011). It is therefore possible that this species might comprise a
‘complex’. The population of Endangered and endemic Bangana
nukta is declining drastically in the study area
as per the local knowledge of fishers. Pollution, overfishing and the
competition created by transplanted carps such as Cirrhinus
mrigala, Labeo rohita, and Labeo catla may also be contributing to the population
decline of B. nukta (Ghate
et al. 2002; Kharat et al. 2003; Dahanukar
et al. 2012). Similarly, Hypselobarbus mussullah assessed as ‘Endangered’ as per IUCN criteria
(Dahanukar & Raghavan 2011) was collected in low
numbers at Bahe. Labeo
potail, a species that has been assessed as
‘Endangered’ due to population decline of 50–60 % in the last 10 years due to
organic and inorganic pollution, exploitation and competition created by
transplanted carps (Dahanukar 2011) was collected
near Palus and Sangli.
However, their numbers are declining rapidly due to pollution from domestic
organic waste and effluents released heavily from industries situated on the
river-bank. Another Krishna River endemic and threatened species, Botia striata
(locally called ‘waghmasa’) (Image 3-22) was recorded
from Bahe, Borgaon and Islampur. At Bahe and Borgaon, indiscriminate collection of this species by
aquarium traders in the summer months is a major threat to the species. The
species is however relatively abundant in the study area, and also in Koyna River (Jadhav et al. 2011).
Gagata itchkeea (Image 3-25) a species recorded
previously from the Krishna River system (Kalwar
& Kelkar 1956; Jayaram 1995; Kharat et al.
2003; Wagh & Ghate
2003; Chandanshive et al. 2007) was collected
from Bahe in very low numbers. Other important endemic
species such as Garra bicornuta,
Parapsilorhynchus discophorus,
Pachypterus khavalchor
were also collected from various sampling sites.
We recorded Labeo
kontius (Image 1) for the first time from the
Krishna River system in, Maharashtra State, through samples from Miraj, thus
extending its range to the northern part of the Western Ghats. Labeo kontius was
described by Jerdon (1849) from Cauvery River and its
tributaries. Currently, the species is also known to occur in the Bhavani and Moyar rivers and their tributaries (Rajan
1955; Manimekalan 1998), as well as in the main
stretch of the Cauvery River (Jayaram et al. 1982; Jayaram & Dhas 2000).
Krishna River harbours a rich
diversity of endemic and threatened fishes of Western Ghats. However, this fauna
is threatened due to overfishing, introduced species, sand mining and organic
and inorganic pollution. If the present anthropogenic impact continues, this
might lead to a drastic decline of habitats and populations of fish species
available in this region. It is therefore essential to declare some stretch of
rivers as aquatic sanctuaries, particularly near Bahe
and Miraj for protection and preservation of endemic and threatened species and
mitigation of anthropogenic stress.
Table 1. List of Freshwater
Fishes collected from the Krishna River, Sangli
District, Maharashtra
|
Order |
Family |
Species |
Status |
WGE |
KRE |
IUCN Red List |
1 |
Anabantiformes |
Channidae |
Channa gachua (Hamilton, 1822) |
M |
- |
- |
LC |
2 |
Channa punctata (Bloch, 1793) |
M |
- |
- |
LC |
||
3 |
Channa striata (Bloch, 1793) |
R |
- |
- |
LC |
||
4 |
Beloniformes |
Belonidae |
Xenentodon cancila (Hamilton, 1822) |
R |
- |
- |
LC |
5 |
Hemiramphidae |
Hyporhamphus limbatus (Valenciennes, 1847) |
R |
- |
- |
LC |
|
6 |
Cichliformes |
Cichlidae |
Oreochromis mossambicus (Peters, 1852) |
C |
- |
- |
|
7 |
Cypriniformes |
Botiidae |
Botia striata Rao, 1920 |
A |
+ |
+ |
EN |
8 |
Cobitidae |
Lepidocephalichthys thermalis (Valenciennes, 1846) |
A |
- |
- |
LC |
|
9 |
Cyprinidae |
Bangana nukta (Sykes, 1839) |
R |
+ |
- |
EN |
|
10 |
Cirrhinus reba (Hamilton, 1822) |
M |
- |
- |
LC |
||
11 |
Cyprinus carpio Linnaeus, 1758 |
R |
- |
- |
|
||
12 |
Garra bicornuta Rao, 1920 |
C |
+ |
+ |
NT |
||
13 |
Garra mullya (Sykes, 1839) |
A |
- |
- |
LC |
||
14 |
Gymnostomus ariza (Hamilton, 1807) |
R |
- |
- |
LC |
||
15 |
Gymnostomus fulungee (Sykes, 1839) |
M |
+ |
+ |
LC |
||
16 |
Hypselobarbus jerdoni (Day, 1870) |
M |
+ |
- |
LC |
||
17 |
Hypselobarbus kolus (Sykes, 1839) |
M |
+ |
- |
VU |
||
18 |
Hypselobarbus mussullah (Sykes, 1839) |
M |
+ |
- |
EN |
||
19 |
Labeo calbasu (Hamilton, 1822) |
M |
- |
- |
LC |
||
20 |
Labeo catla (Hamilton, 1822) |
R |
- |
- |
LC |
||
21 |
Labeo fimbriatus (Bloch, 1795) |
R |
- |
- |
LC |
||
22 |
Labeo kontius (Jerdon, 1849) |
R |
+ |
- |
LC |
||
23 |
Labeo porcellus (Heckel, 1844) |
R |
+ |
- |
LC |
||
24 |
Labeo potail (Sykes, 1839) |
R |
+ |
- |
EN |
||
25 |
Labeo rohita (Hamilton, 1822) |
R |
- |
- |
LC |
||
26 |
Osteobrama neilli (Day, 1873) |
R |
+ |
+ |
LC |
||
27 |
Ostobrama peninsularis Silas, 1952 |
M |
+ |
- |
DD |
||
28 |
Osteobrama vigorsii (Sykes, 1839) |
C |
- |
- |
LC |
||
29 |
Parapsilorhynchus discophorus Hora, 1921 |
R |
+ |
- |
VU |
||
30 |
Pethia sanjaymoluri Katwate, Jadhav, Kumkar, Raghavan & Dahanukar,
2016 |
A |
+ |
+ |
NE |
||
31 |
Puntius chola
(Hamilton,
1822) |
M |
- |
- |
LC |
||
32 |
Puntius sophore (Hamilton, 1822) |
C |
- |
- |
LC |
||
33 |
Rohtee ogilbii Sykes, 1839 |
M |
+ |
+ |
LC |
||
34 |
Systomus sarana (Hamilton, 1822) |
C |
+ |
- |
LC |
||
35 |
Danionidae |
Amblypharyngodon mola (Hamilton, 1822) |
R |
- |
- |
NE |
|
36 |
Devario aequipinnatus (McClelland, 1839) |
C |
- |
- |
LC |
||
37 |
Opsarius bendelisis (Hamilton, 1807) |
M |
- |
- |
LC |
||
38 |
Rasbora daniconius (Hamilton, 1822) |
C |
- |
- |
LC |
||
39 |
Salmostoma acinaces (Valenciennes,
1844) |
C |
+ |
- |
LC |
||
40 |
Salmostoma balookee (Sykes, 1839) |
C |
- |
- |
LC |
||
41 |
Salmostoma bacaila (Hamilton, 1822) |
M |
- |
- |
LC |
||
42 |
Salmostoma boopis (Day, 1874) |
A |
+ |
- |
LC |
||
43 |
Salmostoma novacula (Valenciennes, 1838) |
M |
+ |
- |
LC |
||
44 |
Nemacheilidae |
Indoreonectes cf. evezardi (Day, 1872) |
R |
- |
- |
LC |
|
45 |
Nemacheilus anguilla Annandale, 1919 |
M |
+ |
+ |
LC |
||
46 |
Nemachilichthys rueppelli (Sykes, 1839) |
M |
+ |
+ |
LC |
||
47 |
Paracanthocobitis mooreh (Sykes, 1839) |
A |
|
|
LC |
||
48 |
Schistura denisoni (Day, 1867) |
R |
- |
- |
LC |
||
49 |
Cyprinodontiformes |
Aplocheilidae |
Aplocheilus lineatus (Valenciennes, 1846) |
R |
- |
- |
LC |
50 |
Gobiiformes |
Gobiidae |
Glossogobius giuris (Hamilton, 1822) |
C |
- |
- |
LC |
51 |
Osteoglossiformes |
Notopteridae |
Notopterus synurus (Bloch & Schneider, 1801) |
C |
- |
- |
LC |
52 |
Perciformes |
Ambassidae |
Chanda nama Hamilton, 1822 |
M |
- |
- |
LC |
53 |
Parambassis ranga (Hamilton, 1822) |
M |
- |
- |
LC |
||
54 |
Siluriformes |
Ailiidae |
Proeutropiichthys taakree (Sykes, 1839) |
M |
- |
- |
LC |
55 |
Bagridae |
Hemibagrus maydelli (Rossel, 1964) |
M |
+ |
+ |
LC |
|
56 |
Mystus bleekeri (Day, 1877) |
M |
- |
- |
LC |
||
57 |
Mystus malabaricus (Jerdon, 1849) |
M |
+ |
- |
NT |
||
58 |
Mystus seengtee (Sykes, 1839) |
M |
+ |
- |
LC |
||
59 |
Mystus vittatus (Bloch, 1794) |
R |
- |
- |
LC |
||
60 |
Rita gogra (Sykes, 1839) |
M |
+ |
- |
LC |
||
61 |
Rita kuturnee
(Sykes,
1839) |
M |
+ |
- |
LC |
||
62 |
Sperata cf. aor (Hamilton, 1822) |
C |
- |
- |
LC |
||
63 |
Sperata seenghala (Sykes, 1839) |
M |
- |
- |
LC |
||
64 |
Clariidae |
Clarias gariepinus (Burchell, 1822) |
C |
- |
- |
|
|
65 |
Heteropneustidae |
Heteropneustes fossilis (Bloch, 1794) |
M |
- |
- |
LC |
|
66 |
Horabagridae |
Pachypterus khavalchor (Kulkarni, 1952) |
R |
+ |
+ |
DD |
|
67 |
Pangasiidae |
Pangasius pangasius (Hamilton, 1822) |
R |
- |
- |
LC |
|
68 |
Siluridae |
Ompok bimaculatus (Bloch, 1794) |
C |
- |
- |
NT |
|
69 |
Wallago attu
(Bloch
& Schneider, 1801) |
R |
- |
- |
NT |
||
70 |
Sisoridae |
Glyptothorax cf. poonaensis Hora, 1938 |
R |
+ |
+ |
EN |
|
71 |
Gagata itchkeea (Sykes, 1839) |
R |
+ |
|
VU |
||
72 |
Synbranchiformes |
Mastacembelidae |
Macrognathus pancalus (Hamilton, 1822) |
M |
- |
- |
LC |
73 |
Mastacembelus armatus (Lacepede, 1800) |
C |
- |
- |
LC |
A—Abundant | C—Common |
M—Moderate | R—Rare | EN—Endangered | VU—Vulnerable | NT—Near Threatened |
DD—Data Deficient | LC—Least Concern. Taxonomic status as per Fricke et al.
(2020). Status for invasive alien species are not provided.
For figure & images - - ciick
here
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