Journal of
Threatened Taxa | www.threatenedtaxa.org | 26 June 2018 | 10(7):
11973–11979
Fish fauna of Nandur-Madhmeshwar wetland,
Maharashtra, India
Prashant Wagh 1,Sudhakar Kurhade 2,Shrikant Jadhav 3 & Deepa Jaiswal 4
1,2 New Arts, Commerce and Science College, Ahmadnagar, Maharashtra 414 001, India
3,4 Zoological Survey of India, Freshwater
Biology Regional Centre, Hyderabad, Telangana 500048,
India
1 prashantsinnarkar@gmail.com, 2 sudhakarkurhade@gmail.com, 3 shrikantjadhavzsi@gmail.com (corresponding author), 4 deepajzsi@gmail.com
doi: http://doi.org/10.11609/jott.4246.10.7.11973-11979 | ZooBank:urn:lsid:zoobank.org:pub:D63EF824-7A3E-4E3E-BA60-F7D22F99EC01
Editor: Anonymity
requested. Date of publication: 26
June 2018 (online & print)
Manuscript details: Ms# 4246 | Received 09 May 2018 | Finally accepted 06 June 2018
Citation: Wagh. P., S. Kurhade,
S. Jadhav & D. Jaiswal (2018). Fish fauna
of Nandur-Madhmeshwar wetland, Maharashtra, India. Journal
of Threatened Taxa 10(7): 11973–11979; http://doi.org/10.11609/jott.4246.10.7.11973-11979
Copyright: © Wagh et al. 2018.Creative Commons Attribution 4.0 International License. JoTT allows unrestricted use of this article in any
medium, reproduction and distribution by providing adequate credit to the
authors and the source of publication.
Funding: None.
Competing interests: The authors declare no competing interests.
Acknowledgements: The authors PW and SK are thankful to the
Principal, New Arts, Commerce & Science College, Ahmadnagar for facilities. We are grateful to Dr. Kailash Chandra, Director, Zoological Survey of
India, Kolkata and to Dr.P.S. Bhatnagar, Scientist-D & Officer-in-Charge,
Zoological Survey of India, Western Regional Centre, Pune for facilities and
encouragement.
Nandur-Madhmeshwar Wetland (NMW) is located at Khangaon Thadi Village (20.0080N & 74.1310E),Niphad Tehsil of Nasik District of Maharashtra (Fig.
1). A stone weir was constructed during
1907–1913 across the river Godavari just below the confluence of Kadava and Godavari Rivers at Nandur-Madhmeshwar. The water released from Godavari and
lake Beale (Darna) reservoir is stored at Nandur-Madhmeshwar and subsequently released through canals
for irrigation. Silt and organic
matter that are carried away with water flow accumulate in the lake, due to
which islands and shallow water ponds have been created. This resulted in the biologically
enriched conditions by which aquatic vegetation has been stabilized. Huge amounts of silt have been deposited
in the dam since 1913; consequently much of the lake is now marshland or very
shallow water. Because of its
outstanding ecological, faunal, floral and zoological significance the area was
declared a sanctuary in 1950. The
sanctuary has interspersed grasslands with semi-evergreen forests.
Even
though some studies are available on the fish fauna of Godavari River,
information on the fish fauna of NMW is limited. David (1963) studied fishes of the
Godavari River but did not provide any collection data. Khedkar (2005)
and Yadav (2005b) studied the fishes of Nathsagar wetlands, Jaikwadi on
Godavari River, Paithan, Aurangabad. Recently, Maharashtra Pollution Control
Board and Central Institute of Fishery Education (MPCB & CIFE 2011) studied
the fishes by selecting various sites of the Godavari River including Nandur-Madhmeshwar wetland and reported 24 species from
this wetland. The present study
conducted a detailed survey in the wetland area. The study aims to ascertain the
distribution and abundance of fishes and to identify threats so as to provide
conservation measures.
We
collected the fishes from the wetland (outside the sanctuary area) during
2010–2012. Fishes were
collected by hand net, cast net and also obtained from local fishermen. Fishes were preserved in 4% formalin and
identified using available literature (Jayaram 1991,
2010; Menon 1987, 1992; Talwar& Jhingran 1991; Jayaram& Dhas 2000; Jayaram& Sanyal 2003). The fish specimens are deposited in the
museum collection of the Western Regional Centre, Zoological Survey of India,
Pune (Accession No. ZSI/WRC P/5397 to P/5435). Assuming that the fishing effort for a
given type of net was constant, the relative abundance of the fish was grossly
classified into four categories as given by Dahanukaret al. (2012), namely abundant (76–100 % of the total catch), common
(51–75 % of the total catch), moderate (26–50 % of the total
catch), and rare (1–25 % of the total catch).
Thirty-nine
fish species belonging to seven orders, 14 families and 30 genera were recorded
from the study area (Table 1). Cypriniformes was the most dominant order contributing 20
species followed by Perciformes seven, Siluriformes seven, Synbranchiformestwo and Osteoglossiformes, Anguilliformesand Beloniformes one species each. Cyprinidae was
the most dominant family representing 17 species followed by Channidae three and Bagridaethree. Some of the fishes collected
from NMW are shown in Image 1. Of
the total fish species obtained, 19 fish species were found to be common, out
of which 11 had a uniform distribution throughout the study period in different
months. Sixteen species showed
moderate abundance while one was rare. Three invasive alien species were also recorded from the study area
namely, Cyprinus carpio,Clarias gariepinusand Oreochromis mossambicus. The introduction of alien species causes
serious threat to native fish fauna with regards to competition for food,
predation and disruption of the aquatic food chain (Daniels 2006; Raghavan et al. 2008; Knight 2010). The list includes typical primary
freshwater fishes.

The
fish diversity in NMW is high as compared to various protected areas in
Maharashtra such as Sanjay Gandhi National Park (S=14) (Singh & Yazdani 1988), Pench National
Park (S=33) (Yadav 2004), NathsagarWetland (S=33) (Yadav 2005b), BhimashankarWildlife Sanctuary (S=21) (Yadav & Jadhav 2009), RadhanagariWildlife Sanctuary (S=20) (Jadhav & Jadhav 2014a), Chandoli National
Park (S=11) (Jadhav & Jadhav2014b), and low as compared to Ujani Wetland (S=54) (Yazdani & Singh 2002), MelghatTiger Reserve (S=96) (Yadav, 2005a), Tadoba-Andhari Tiger Reserve (S=84) (Yadav2006). The number of fish species
is higher than those recorded by MPCB & CIFE (2011) from this wetland.
Notopterus notopterus is quite common in some areas of the
wetland. Some specimens of N. notopterus resemble Chitala chitala externally, hence MPCB & CIFE (2011)
presumably consider them as C. chitala, but
our study suggests that it is just the lack of understanding of taxonomy and
incorrect identification of species. C. chitalarecords from Maharashtra are misidentifications of N. notopterusand C. chitala is distributed only in the
Ganges and Brahmaputra basins of northern India (see Chaudhry2010). The two species of genus Salmostoma, namely, S. bacailaand S. balookee are abundant in rainy season
and found in turbid waters where vegetation is rich. Rasbora daniconius and Devario malabaricus have been found in adjacent canals
and rocky pools. Both the species
are common. The specimens of Puntius amphibius, P.sophore, P. chola,
and Pethia conchoniuswere caught from the adjacent canals, rocky pools and from the banks of the
river where grassy vegetation is abundant, but these species have low food
value in the local market. MPCB
& CIFE (2011) reported Pethia shalynius and P. phutuniofrom the study area, but we could not collect these two species from the study
area. Further, we collected some
specimens of P. conchonius having dark bases
on their scales and the dark spots coalesce with these dots. Presumably, MPCB
& CIFE (2011) in their list designated these specimens as P. shalynius, but at present, on the basis of
morphological characters we consider them as P. conchonius. In spite of that, P. shalynius is endemic to Manipur, northeasternIndia and our observations suggest that this species is not present in this
wetland.
The
Critically Endangered Parapsilorhynchus prateri (Dahanukar 2011) reported
by MPCB & CIFE (2011) from NMW is quite interesting. We could not collect P. prateri from this wetland. The species is truly hill stream and its
occurrence in NMW needs confirmation. Although Labeo rohitaand Catla catlaare commercially significant in the local market, their population in the area
is rare. Further, our observations
indicate that in this wetland there are very good populations of fish species,
namely: Ompok bimaculatus,Wallago attu,Notopterus notopterus, Mystus malabaricus, Mastacembelus armatus, Heteropneustes fossilis, Channa punctata, Channa marulius and Garra mullya. We have also collected two specimens of
Spotted Snakehead albino fish Channa punctata, which is already reported elsewhere (see Jadhav et al. 2013).
MPCB
& CIFE (2011) reported 24 species from NMW, out of which nine species were
not recorded in our study namely: Chitala chitala, Pethia shalynius, P. phutunio, Ompok malabaricus, Parapsilorhynchus prateri, Salmostoma novacula, Rasbora labiosa, Macrognathus aral, and Strongylura strongylura. The occurrence of the species C. chitala, P. shalynius, P. prateri, and S. strongylura needs confirmation as stated earlier. S. strongylura is
a marine species and does not come that far inland and is likely a
misidentification of Xenentodon cancila. Nevertheless, in our study 21 species were reported for the first time
from this wetland. Out of these, 15
species were identified as commercially important and fetch a good market
price. One of the greatest assets
of this wetland is not only is it a good habitat for birds but also provides
good fishing opportunities for fishers and also for local tribalsfor their livelihood.
The
fish fauna of the wetland is threatened due to introduced species as well as
anthropogenic activities. Heavy
siltation is causing the reservoir to fill up gradually. Excessive fishing and
grassland patches of the sanctuary area are overgrazed by domestic buffaloand cattle facilitate the spread of invasive alien plants. Invasion by exotic plants Eichhornia crassipesand Parthenium sp. is serious and need to be
removed. Diesel engines, which are
used along with electric pumps to draw water, cause immense pollution in the
area (Kumar et al. 2002). The
avifauna of the area is considerably disturbed because of blasting undertaken
in the area for mining purposes. The reservoir surroundings are intensively cultivated for wheat, maize,
sugarcane and vegetables. For the
conservation of the valuable biodiversity of the wetland, awareness programmes
should be conducted among the local people. Grazing activities in the wetland area
should be controlled. To protect
these ecologically important areas, the surrounding areas need to be declared
as an eco sensitive area, for the better conservation of biodiversity.
Table 1. List of freshwater fish species
recorded from Nandur-Madhmeshwar Wetland in the
present study.
|
Order/Family/Scientific name |
IUCN status |
Relative abundance |
|
Order: Osteoglossiformes |
|
|
|
Family: Notopteridae |
|
|
|
Notopterus notopterus (Pallas, 1769) |
LC |
C |
|
Order: Anguilliformes |
|
|
|
Family: Anguillidae |
|
|
|
Anguilla bengalensis (Gray, 1831) |
LC |
R |
|
Order: Cypriniformes |
|
|
|
Family: Cyprinidae |
|
|
|
Salmostoma balookee (Sykes, 1839) |
LC |
M |
|
Salmostoma bacaila (Hamilton, 1822) |
LC |
M |
|
Devario malabaricus (Jerdon,
1849) |
LC |
C |
|
Rasbora daniconius (Hamilton, 1822) |
LC |
C |
|
Amblypharyngodon mola (Hamilton, 1822) |
LC |
M |
|
Cyprinus carpio Linnaeus, 1758 |
EX |
M |
|
Puntius amphibius (Valenciennes,
1842) |
DD |
M |
|
Puntius chola (Hamilton, 1822) |
LC |
M |
|
Systomus sarana subnasutus (Valenciennes, 1842) |
LC |
M |
|
Puntius sophore (Hamilton, 1822) |
LC |
C |
|
Pethia conchonius (Hamilton, 1822) |
LC |
C |
|
Hypselobarbus curmuca (Hamilton, 1807) |
VU |
M |
|
Cirrhinus reba (Hamilton, 1822) |
LC |
M |
|
Labeo boggut (Sykes, 1839) |
LC |
M |
|
Labeo calbasu (Hamilton, 1822) |
LC |
M |
|
Labeo rohita (Hamilton, 1822) |
LC |
M |
|
Garra mullya (Sykes, 1839) |
LC |
C |
|
Family: Nemacheilidae |
|
|
|
Schistura denisoni (Day, 1867) |
LC |
M |
|
Indoreonectes evezardi (Day, 1872) |
LC |
M |
|
Family: Cobitidae |
|
|
|
Lepidocephalichthys thermalis (Valenciennes,
1846) |
LC |
C |
|
Order: Siluriformes |
|
|
|
Family: Bagridae |
|
|
|
Mystus bleekeri (Day, 1877) |
LC |
C |
|
Mystus cavasius (Hamilton, 1822) |
LC |
C |
|
Mystus malabaricus (Jerdon, 1849) |
NT |
M |
|
Family: Siluridae |
|
|
|
Ompok bimaculatus (Bloch, 1794) |
NT |
C |
|
Wallago attu (Bloch & Schneider, 1801) |
NT |
C |
|
Family: Clariidae |
|
|
|
Heteropneustes fossilis (Bloch, 1794) |
LC |
A |
|
Clarias gariepinus (Burchell,
1822) |
EX |
C |
|
Order: Beloniformes |
|
|
|
Family: Belonidae |
|
|
|
Xenentodon cancila (Hamilton, 1822) |
LC |
M |
|
Order: Synbranchiformes |
|
|
|
Family: Mastacembelidae |
|
|
|
Macrognathus pancalus Hamilton, 1822 |
LC |
C |
|
Mastacembelus armatus (Lacepede,
1800) |
LC |
C |
|
Order: Perciformes |
|
|
|
Family: Ambassidae |
|
|
|
Chanda nama Hamilton, 1822 |
LC |
C |
|
Parambassis ranga (Hamilton, 1822) |
LC |
C |
|
Family: Cichlidae |
|
|
|
Oreochromis mossambicus (Peters, 1852) |
EX |
C |
|
Family: Gobiidae |
|
|
|
Glossogobius giuris (Hamilton, 1822) |
LC |
C |
|
Family: Channidae |
|
|
|
Channa gachua (Hamilton, 1822) |
LC |
C |
|
Channa punctata (Bloch, 1793) |
LC |
A |
|
Channa marulius (Hamilton, 1822) |
LC |
A |
Abundance categories: A - Abundant, C -
Common, M - Moderate, R - Rare; EX - Exotic, S - Number of species IUCN (2013):
LC - Least Concern, NT - Near Threatened, DD - Data Deficient, VU -
Vulnerable. Taxonomic status as perEschmeyer et al. (2016)


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