World Journal of Fish and Marine Sciences 7 (1): 21-28, 2015
ISSN 2078-4589
© IDOSI Publications, 2015
DOI: 10.5829/idosi.wjfms.2015.7.1.92103
Indigenous Freshwater Piscine Resources of
Indian Sundarban Biosphere Reserve: Status and Prospects
1
Sourabh Kumar Dubey, 1Raman Kumar Trivedi and 2Bimal Kinkar Chand
1
Department of Aquatic Environment Management, Faculty of Fishery Sciences,
West Bengal University of Animal and Fishery Sciences, 5 Budherhat Road, Kolkata-700094, India
2
Directorate of Research, Extension and Farms,
West Bengal University of Animal and Fishery Sciences, Kolkata-700037, India
Abstract: Study of indigenous piscine resources is utmost important because these fish species in its natural
setting serves as ecological indicators. This contribution focuses on diversity and conservation aspects of
freshwater indigenous fish resources of Indian Sundarban Biosphere Reserve. The study revealed the
occurrence of 62 ichthyofauna belonging to 45 genera, 28 families and 9 orders. Of these fishes, 6% fish
belonged to Endangered category and 2% were Vulnerable and Critically Endangered category. This article also
addresses the culture potential of the small indigenous fishes as well as threat and conservation issues.
Key words: Indigenous Fish
Fish Diversity
Sundarban Biosphere Reserve
Conservation
low-lying islands, of which 48 islands are occupied by
human habitation in 5,363 km2 area. On the Indian side, it
extends 19 community development blocks over two
districts; 13 blocks in South 24 Parganas and 6 blocks
in North 24 Parganas districts with total 190 Gram
Panchayats and 1064 villages. The freshwater flows from
the mainstream rivers and the tidal ingress from the sea
result in a gradient of salinity that varies both spatially
and temporally within the Biosphere Reserve. In general,
the salinity is higher nearer the coast and the water in the
inland side boundary of the Sundarban is nearly fresh [5].
Freshwater domains closed to blind rivers, creeks and
canals in the Sundarban biosphere are about 891 km 2.
The Sundarban biosphere Reserve is endowed with a vast
expanse of often inland waters in the form of canals,
estuaries, lakes, ponds, tanks, wetlands and paddy fields
etc which always attracted attention for its cosmic aquatic
recourses with rich indigenous fish diversity. Although
the total estuarine habitat occupy a significant component
available to fishes and play important roles as nursery and
foraging grounds. The rural population, specially the rural
poor, are dependent to varying degrees on these fishery
resources for their livelihoods, income and food. It is well
known that small indigenous fish species is significantly
INTRODUCTION
The inland water resources of India are renowned
for their heterogeneity in fish diversity as for as their
magnificent productive potential. India is the one of the
mega-biodiversity countries in the world and occupies
9th position in terms of freshwater mega-biodiversity [1].
The Indian fish fauna is an assemblage of about 2500
species depicting diverse characteristics, of which 930
species belonging to 326 genera, inhabit the inland waters
[2] and 1570 are found in marine water [3]. Out of these,
400 species are commercially important, which include
cultured, cultivable and wild species. Globally, Indian fish
represents 11% of total species, 24% of total genera and
57% of the total families [4].
The Indian Sundarban Biosphere
Reserve
(between 21°40'N and 22°40'N, lat. and 88°03'E and
89°07'E long.) is a UNESCO declared World heritage Site,
lies on the southern fringes of the West Bengal state of
India, where the Gangetic plain meets the Bay of
Bengal. The Sundarban, world’s largest mangrove
ecosystem, is an archipelago of several hundred islands,
spread across 9,630 km2 in India and 16,370 km2 in
Bangladesh. The Indian Sundarban delta comprises of 102
Corresponding Author: Sourabh Kumar Dubey, Department of Aquatic Environment Management, Faculty of Fishery Sciences,
West Bengal University of Animal and Fishery Sciences, 5 Budherhat Road, Kolkata-700094, India.
E-mail: sourabhkumardb@gmail.com.
21
World J. Fish & Marine Sci., 7 (1): 21-28, 2015
contributed global food security through its high quality
vitamin and mineral sources [6, 7], however very less
interest has been rewarded on their role in production
enhancement, processing, captive breeding and
conservation approaches. Subsequently
in Indian
Sundarban coastal biome, many indigenous fishes has
become a major concern due to its constant environmental
changes, over exploitation of resources, habitat
destruction,
pollution,
demographic
pressure,
introduction of exotic varieties, modern agriculture etc
which might be responsible for species turn over.
Thus, knowledge on species and communities can reveal
crucial facts necessary to the management of the
ecosystems as well as to the identification of important
genetic resources.
Documentations on indigenous fish resources from
West Bengal were carried out by several workers [8-10].
Various workers explored estuarine, marine piscine
resources from water of Indian Sundarban in a scattered
way [11-15]. However, detail documentations on
freshwater indigenous fish resources of Indian Sundarban
biosphere are really scanty. In continuation to the fact,
the present works deals with an aim to explore available
freshwater indigenous fish fauna from Indian Sundarban
Biosphere.
were associated with this survey (Paribesh Unnayan
Parishad for Sagar block and Joygopalpur Gram Vikash
Kendra for Basanti block).
Sampling Methodology: During the survey period, fish
specimens have been collected using different kinds of
nets (hand net, gill net, scoop net and cast net) from
almost all kinds of waterbodies like canals, beels, derelict
waterbodies, ponds and road side ditches. Sampling has
been conducted during early morning in between 6 to 8
AM involving the local fishermen. After collection, all the
fishes captured have been immediately segregated
according to their family. Those species was not identified
in field, were preserved in 10% formaldehyde and brought
to laboratory for further investigations. Identifications
were made after following standard literatures [2, 16-18].
Conservation status of the fishes was determined
according to CAMP report [19], National Bureau of Fish
Genetic Resources [20] and IUCN Red list of Threatened
Species [21]. Farmer’s perceptions on loss of indigenous
fish diversity were noted based on cross-sectional
questionnaire-based survey and focused group
discussion (FGD). Threat ranks of fishes were established
in 1-10 ranked hypothetical scale.
RESULTS
MATERIALS AND METHODS
From the present short span study, total 62
ichthyofauna belonging to 45 genera, 28 families and 9
orders have been recorded from the two blocks of Indian
Sundarban Biosphere Reserve (Table 1). Order
perciformes represented maximum number of species
distribution followed by siluriformes, cypriniformes and
synbranchiformes (Figure 1). Family wise species
heterogeneity was conspicuous and cyprinidae family
demonstrated maximum number of individuals (13 species)
followed by bagridae (6 species), channidae and gobidae
(5 species each). Family siluridae, mastacembelidae and
osphronemidae represented 3 individuals respectively.
Likewise family ambassidae, notopteridae and
tetraodontidae represented 2 individuals respectively,
whereas 18 families were found to share only 1 individual
species (Figure 2). It is noted that out of 62 numbers of
species, 17 fish species (family bagridae, gobidae,
tetraodontidae, eleotridae, anguillidae, plotosidae,
belonidae) have been encountered from both freshwater
and brackish water region. The present set of data also
revealed that out of 62 species, 6% indigenous fish
belonged to Endangered category and 2% were
Study Area: A rapid survey work has been conducted for
collecting and or recording the available indigenous
freshwater fish fauna in two selected deltaic blocks of
Indian Sundarban Biosphere Reserve namely Basanti and
Sagar block under district South 24 Parganas during the
months of September to December, 2011. The largest
deltaic block, Sagar Island is located in the extreme
western sector of Sundarban lies between 21°53' N and
88°02' to 88°15' E. This island with an area of around 300
km² is surrounded by two rivers, Hoogly and Muriganga.
Both the rivers meet Bay of Bengal on either side of the
Sagar Island and are totally disconnected from mainland.
Basanti is located in the eastern part of Indian Sundarban
biosphere lies between 22°11'21?N and 88°40'14?E with an
area of 286.03 km2. It is bounded by the Matla and
Vidyadhari rivers and numerous creeks. Both islands are
surrounded by century old man made embankments which
possible freshwater sphere within the land masses. 20
Gram Panchayats in the 2 blocks were covered during this
survey (9 Gram Panchayats in Sagar block, 11 Gram
Panchayats in Basanti block) and two reputed local NGOs
22
World J. Fish & Marine Sci., 7 (1): 21-28, 2015
Table 1: Checklist of indigenous freshwater ichthyofauna of Sundarban Biosphere Reserve with their endemic status
Sl
Order
Family and Scientific name
Cypriniformes
Cyprinidae
Amblypharyngodon mola (Hamilton)
Brachydanio rerio (Hamilton)
Chela laubuca (Hamilton)
Puntius conchonius (Hamilton)
Puntius phutunio (Hamilton)
Systomus sarana (Hamilton)
Puntius sophore (Hamilton)
Puntius terio (Hamilton)
Esomus danricus (Hamilton)
Rasbora daniconius (Hamilton)
Pethia gelius (Hamilton)
Pethia ticto(Hamilton)
Salmostoma bacalia (Hamilton)
Cobitidae
Lepidocephalus guntea (Hamilton)
Aplocheilidae
Aplocheilus panchax (Hamilton)
Belonidae
Xenentodon cancila (Hamilton)
Bagridae
Mystus cavasius(Hamilton)
Mystus gulio(Hamilton)
Mystus tengara (Hamilton)
Mystus vittatus (Bloch)
Sperata aor (Hamilton)
Sperata seenghala (Sykes)
Siluridae
Ompok pabda (Hamilton)
Ompok bimaculatus (Bloch)
Wallago attu (Schneider)
Plotosidae
Plotosus canius (Hamilton)
Schilbeidae
Ailia coila (Hamilton)
Pangasidae
Pangasius pangasius (Hamilton)
Sisoridae
Bagarius bagarius (Hamilton)
Clariidae
Clarias batrachus (Linnaeus)
Heteropneustidae
Heteropneustes fossilis (Bloch)
Ophichthidae
Pisodonophis boro (Hamilton)
Anguillidae
Anguilla bengalensis (Gray)
Muraenesocidae
Muraenesox cinereus (Forsskål)
Mastacembelidae
Mastacembelus armatus (Lecepede)
Macrognathus aral (Bloch)
Macrognathus panculus (Hamilton)
Synbranchidae
Amphipnous cuchia (Hamilton)
Channidae
1
2
3
4
5
6
7
8
9
10
11
12
13
14
Cyprinodontiformes
15
Beloniformes
16
Siluriformes
17
18
19
20
21
22
23
24
25
26
27
28
29
30
31
Anguilliformes
32
33
34
Synbranchiformes
35
36
37
38
Perciformes
Vernacular name
23
Mourola
Anju
Dankena
Kunchon Punti
Sar Punti
Deshi Punti
Teri punti
Darikhana
Darikhana
Gili punti
Tit Punti
Conservation status
LRlc
LRnt
LRlc
VU
LRlc
VU
LRnt
LRnt
LRlc
LRlc
LC
LRnt
LRlc
Gunte
LC
Trichokha
LC
Bogo
LRnt
Kabasi tangra
Nona Tangra
Tangra
Sona Tangra
Aor
Aor
LRnt
LC
LC
VU
VU
LC
Pabda
Pabda
Boal
EN
NT
LRnt
Kan magur
NE
Kajri
VU
Pangus
CR
Bag mach
VU
Magur
VU
Singi
VU
Baim
LC
Sona Bam
EN
VU
Bam/Pankal
Tara bam
Tora/Pankal
LC
LRnt
LRnt
Cuche
LRnt
World J. Fish & Marine Sci., 7 (1): 21-28, 2015
Table 1: Continue
39
Channa gachua (Hamilton)
Chang
VU
40
Channa marulius (Hamilton)
Sal/Gajal
LRnt
41
Channa orientalis (Bloch)
Ulko
VU
42
Channa punctata (Bloch)
Lata
LRnt
43
Channa striata (Bloch)
Sol
LRlc
Pod Koi
VU
Nadosh /Veda
LRnt
Gang Bele
LRnt
Badidae
44
Badis badis (Hamilton)
Nandidae
45
Nandus nandus (Hamilton)
Gobidae
46
Boleophthalmus boddarti (Pallas)
47
Glossogobius giuris (Hamilton)
NE
48
Stigmatogobius sadanundio (Hamilton)
49
Pseudapocryptes lanceolatus (Cuvier)
Gule
LC
50
Odontamblyopus rubicundus (Hamilton)
Lal chewa
NE
Kalo Bele
LC
NE
Eleotridae
51
Eleotris fusca (Forster)
Ambassidae
52
Chanda nama(Hamilton)
Kath Chanda
NE
53
Parambassis ranga (Hamilton)
Lal Chanda
LC
Koi
VU
Anabantidae
54
Anabas testudineus (Bloch)
Polynemidae
55
Polynemus paradiseus (Linnaeus)
Topse
Osphronemidae
56
Trichogaster fasciata (Schneider)
Kholse
57
Trichogaster lalius(Hamilton)
Lal Kholse
NE
58
Trichogaster chuna (Hamilton)
Chuno Kholse
NE
Osteoglossiformes
LRnt
Notopteridae
59
Chitala chitala (Hamilton)
Chitol
EN
60
Notopterus notopterus (Pallas)
Pholui
LRnt
Tetraodontiformes
Tetraodontidae
61
Tetraodon cutcutia (Hamilton)
Tepa
LRnt
62
Tetraodon fluviatilis (Hamilton)
Potka
LRnt
CR: Critically endangered; EN: Endangered; LC: Least Concern; LRlc: Lower risk-least concern; LRnt: Lower risk-near threatened; NE: Not Evaluated; NT:
Near Threatened; VU: Vulnerable
Fig 1: Order wise distribution of indigenous freshwater fishes of Sundarban Biosphere Reserve
24
World J. Fish & Marine Sci., 7 (1): 21-28, 2015
Fig 2: Family wise number of indigenous freshwater fishes of Sundarban Biosphere Reserve
Fig 3: Conservation status of indigenous freshwater fishes of Sundarban Biosphere Reserve
Vulnarable and Critically Endangered category. However,
37 % species belonged to Lower Risk-Near Threatened
category (Figure 3).
The freshwater food fishes and their fishery occupied
an important portion in Sundarban Biosphere Reserve.
The fishes are mostly belonged to order cypriniformes,
perciformes and siluriformes. The cypriniformes includes
both major and minor carps. At the time of field survey it
has been observed that, the major indigenous carp
species viz., Labeo rohita (Hamilton), Catla catla
(Hamilton) and Cirrhinus mrigala (Hamilton) along with
three exotic carps mainly Cyprinus carpio (Linnaeus),
Ctenopharyngodon
idella,
(Valenciennes)
and
Hypophthalmichthys molitrix (Valenciennes) were widely
cultured. Farmers also stocked minor carps like Labeo
bata (Hamilton), Labeo calbasu (Hamilton) along with
Indian major carps. Other exotic varieties like Barbodes
gonionetus (Bleeker), Hypophthalmichthys nobilis
(Richardson), Oreochromis mossambicus (Peters),
Oreochromis niloticus (Linnaeus) were very popular.
In recent years, invasive alien species like Pygocentrus
nattereri (Kner), Clarius gariepinus (Burchell) were
introduced in Sundarban region and cultured in
freshwater pond along with other fish. During the study
period, it has been observed that freshwater indigenous
carps also cultured and grew nicely in slight brackish
water (> 10 ppt salinity). Among small indigenous fishes,
most of them are natural breeders and can easily breed
during the period of monsoon and grow up with the carps.
Indigenous brackish water fishes like Lates calcarifer
(Bloch), Chelon (Liza) parsia (Hamilton), Chelon
planiceps (Liza tade) (Valenciennes), Chelon (Liza)
macrolepis (Smith), Mugil cephalus (Linnaeus),
Rhinomugil corsula (Hamilton), Etroplus suratensis
(Bloch), Scatophagus argus (Linnaeus), Toxotes
chatareus (Hamilton), Terapon jarbua (Forsskal) etc were
found abundantly in freshwater areas and few of them
were widely cultured in freshwater ponds in Sundarban
region.
Based on survey, some small indigenous fish species
are noted out, which populations are drastically reducing
since last thirty years. Farmers were rated threat rank of
25
World J. Fish & Marine Sci., 7 (1): 21-28, 2015
Table 2: Threat rank of some indigenous fishes: Farmer’s perception on loss of indigenous fish diversity since last 30 years at Sagar and Basanti block of
Indian Sundarban
Sagar
----------------Threat Rank
Name of Fish
C. gachua
W. attu
C. batrachus, H. fossilis
S. sarana
O. pabda
C. marulius, C.striata, C. punctata
N. nandus
A. bengalensis
A. testudineus
A. mola
Name of Fish
I
II
III
IV
V
VI
VII
VIII
IX
X
N. nandus
W. attu
C. marulius, C.striata, C. punctata
A. testudineus
C. gachua
A. bengalensis
C. nama
C. batrachus, H. fossilis
S. sarana
T. fasciata
each species on 1-10 ranked hypothetical scale which are
listed in Table 2. According to the farmers of Sagar Island,
Channa gachua was ranked first and Amblypharyngodon
mola was ranked last based upon their availability status.
In Basanti block, Nandus nandus was ranked first and
Trichogaster fasciata was ranked last based upon their
availability status.
Basanti
--------------Threat Rank
I
II
III
IV
V
VI
VII
VIII
IX
X
in India, about 23% (104 species) are highly important as
food and aquarium trade and provides local livelihood
security [24].
However, over exploitation of bio resources, ever
expanding population pressure, pollution etc is threatened
Sundarban day by day. In addition to this, temperature
variability, climate induced sea level rise and subsequent
erosion coupled with frequent extreme weather events,
increasing salinity level etc has a serious and emergent
problem in Indian Sundarban over the past two decades
[25]. Due to salinity intrusion in freshwater areas, many
freshwater fish species are subjected to severe stress and
threat due to their inability to cope up with such extreme
conditions. These may have serious impacts on the
distribution, feeding regimes, breeding periodicity of
indigenous freshwater fish gene pool of Sundarban.
Lethal effect of salinity on two small indigenous species,
A. Mola and P. ticto from Indian Sundarban was already
noted by Dubey et al. [26]. Invasive alien fish species has
been emerging as a growing threat to biodiversity of small
indigenous fishes, as some are highly carnivorous and
predatory [27-28]. In this back drop, achieving sustainable
utilisation of indigenous fishes, appropriate planning for
conservation and management strategies are of utmost
importance.
Among the indigenous fishes, many species have
wider potentialities as a candidate species in freshwater
aquaculture domain. These are mainly A. mola,
N. notopterus, C. chitala, O. pabo and Puntius group.
Murrels (Channa spp.) and air breathing fishes like
A. testudineus, C. batrachus and H. fossilis are becoming
a candidate species for aquaculture in India and also
fetching high price in domestic markets. Non-air breathing
cat fishes like M. cavasius, M. vittatus, M. tengara, S. aor
etc also attracted attention for culture due to their growth
DISCUSSION
Marine and freshwater catches are dominated by a
great diversity of small species [22]. On the contrary,
aquaculture is characterized by production of a limited
number of large freshwater fish species. Owing food
security, lowering of indigenous freshwater fish diversity
is now global concern in many developing countries.
In neighboring country Bangladesh, 15% of species
reported to have disappeared, 20% critically endangered
and the rate of disappearance increasing in recent years
due to various reasons [23].
A total number of 62 indigenous fishes occurring in
freshwater zones of Sundarban Biosphere Reserve were
recorded from the present short span study. In earlier
study, Sen [11] reported 61 finfish species, Mandal and
Nandi [12] documented 141 species under 100 genera,
Nandi et al. [13] reported 76 species belonging to 28
family and Bose et al. [15] reported 74 species. Recently,
Basu et al. [9] reported 52 indigenous freshwater fishes
from South 24 Parganas district alone. This indicates a
good health of freshwater indigenous fish co-occurring in
Indian Sundarban region. Noteworthy, among
documented fishes from the present investigations,
maximum species have ornamental value which has been
already noted by various authors [9-10]. Based on the
assessment of NBFGR, among 450 small indigenous fishes
26
World J. Fish & Marine Sci., 7 (1): 21-28, 2015
and market value [24]. Based on wild seed collection,
some of the fishes are being cultured in small scale.
For large scale propagation, proper seed production
technology and scientific farming is needed to be
popularized and diversified in Sundarban area. It is also
noted that, successful artificial breeding of several
species like A. Mola, N. notopterus, C. chitala, O. pabo,
M. Vittatus, M. gulio, S. sarana, C. batrachas,
A. testudineus, N. nandus were achieved [29-31].
Maintaining piscine diversity is important because
fish species in its natural setting serves as ecological
indicators. To conserve and augment the sustainability
of indigenous fishes in Sundarban Biosphere Reserve,
research and policy framework is essential for
diversification of potential cultivable indigenous fishes.
In situ and ex situ conservation practice is need to be
developed in various pockets of Sundarban to protect the
native fish gene pool. In addition to this, through creating
freshwater aquatic sanctuaries (FAS) within the protected
area, public awareness can be expanded.
2.
3.
4.
5.
6.
7.
CONCLUSION
It can be concluded
that Indian Sundarban
Biosphere Reserve sustains a unique and wealthy
resources of freshwater indigenous ichthyofauna. Owing
various exploitation parameters, sustainable management
and artificial propagation might be a suitable process for
future protection and conservation of small indigenous
fishes as well as food security of local people inhabiting
in Sundarban.
8.
9.
10.
ACKNOWLEDGEMENTS
11.
The authors are grateful to Indian Council of
Agricultural Research (ICAR), New Delhi for the financial
assistance granted for this study through NICRA
(National Initiatives on Climate Resilient Agriculture)
project entitled “Development of Climate Resilient
Aquaculture Strategies for Sagar and Basanti Blocks of
Indian Sundarban”. We are grateful to the authority of
S.D. Marine Biological Research Institute, Sagar Island,
for sharing field laboratory facility.
12.
13.
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