Sahyadri Mathsya
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Sreekantha
Energy & Wetlands Research Group, Centre for Ecological Sciences,
Indian Institute of Science, Bangalore - 560 012.
E-mail: sreekantha@ces.iisc.ernet.in

Sreekantha
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The Western Ghats, extending for over a length of 1600km, lying parallel to the coast hardly 50km away, form one of the magnificent escarpments of late Tertiary age. Except for a short gap near Palghat, it is unbroken throughout its length. The marked diversity of landscape, the youthful character of the rivers, the precipitous escarpments, the narrow gorges and the relative high elevation of the plateau compared to the plains (Radhakrishna, 1991) are the key geographical features of these Ghats.

The Western Ghats, one among the 25 global hotspots of biodiversity, harbours very rich flora and fauna. There are records of over 4,000 species of flowering plants (38% endemism), 330 butterflies (11% endemic), 156 reptiles (62% endemism), 508 birds (4% endemism), 120 mammals (12% endemism) (Daniels, 2003), 290 fishes (41% endemism) (Dahanukar et al, 2004); (Babu and Nayar, 2004) and 131 amphibians (75% endemism) (Gururaja, 2004). The varied climate and diverse topography create a wide array of habitats that support unique sets of plant and animal species. The level of endemism is high and the region is considered one of the world's biodiversity hotspots (Menon and Bawa, 1997).

Fishes-most diverse, yet most neglected

Fishes are the most numerous vertebrates living on this earth and worldwide there are over 25000 species of fishes. Of this about 48% live in freshwaters that constitute just 0.01% of the earth's water. Freshwater fish diversity is unevenly distributed on this planet. The species richness is high in tropical region compared to other parts of the earth. Usually these regions are characterized by high levels of endemism. The world's major rivers like Amazon, Congo, Nile, etc. are some of the pristine rivers of the world with respect to freshwater fish diversity. I t has been estimated that the river Amazon and its tributaries may together harbour 3000 or more species of fishes. Such species-rich areas are called ‘hotspots' and dominate other patterns or trends. Probably the climatic conditions of the tropical region are more stable compared to the temperate regions of the world. This could be one of the favourable conditions for the growth, survival and evolution for the species in tropical regions.

While a great deal of attention has been given to the loss of biodiversity in tropical rain forests, or in coastal areas, the diversity of and within freshwaters has been widely neglected. There is little doubt that freshwater fishes represent the most threatened set of vertebrates (Leveque, 1997). In classifying the worlds' top 25 biodiversity hotspots, vertebrate group was considered excluding fish. This is mainly because of the poorly available data wherein the author (Myer et al 2000) predicts that there could be at least 5,000 species waiting to be discovered among fish, which is more than all mammals.

FRESHWATER FISH DIVERSITY OF WESTERN GHATS

Several attempts have been made to compile a checklist of freshwater fishes of the Western Ghats. These attempts mainly focused on evolving with a comprehensive checklist of freshwater fishes, which is an out come of the patchy (may be of a river basin, a region in the Western Ghats, an administrative boundary within the Western Ghats, etc) taxonomic information available on the diversity of freshwater fishes. Daniels (2001) has listed 218 species from the Western Ghats of which 114 (52%) are endemic to Western Ghats. However, this report lacks a detailed checklist of fishes found in the Western Ghats. The subsequent checklist (Shaji et al 2001) listed 287 fishes with names of individual species. This compilation considered certain estuarine fishes that are found to ascend freshwater for longer distances. The list highlighted the presence of 67% endemic species and 18 exotic or transplanted to the region. The most recent information available is by Dahanukar et al 2004 that lists 288 freshwater fishes, of which 118 (41%) are endemic to Western Ghats. The threat status of fishes found in Western Ghats suggests that at least 41% of fish fauna is threatened by either being vulnerable, endangered, or critically endangered. This study also necessitates the implication of potent conservation measures to conserve the fish fauna of Western Ghats.

Present scenario

Present compilation of the checklist (Annexure) of the freshwater fishes in Western Ghats region lists 318 species of which 42.8% (136 species) are endemic to the region. Of this about 27 species are critically endangered and 55 endangered while 128 are data deficient. Altogether, 39.1% (123 species) of the freshwater fishes come under the category of critically endangered, endangered and vulnerable (Figure 1). Of the 27 critically endangered species 24 are endemic to the region. Similarly, of the 55 endangered species, 37 are endemic. Yet 49 endemic species are data deficient. A comparison of IUCN status between endemic and non-endemic species has been made in figure 2, which clearly shows that the endemic species comprises more of threatened species and the non-endemic comprise more of generalist species in Western Ghats.

Figure 1. Species composition with respect to IUCN status

Figure 2. Comparison of the IUCN status between endemic and non endemic groups of fish species

DIVERSITY OF HABITATS IN WESTERN GHATS

The Western Ghats gifted with perennial streams outlines the unique habitats for the fishes. They run for about 1600 km from north to south and are drained by 38 east flowing and 27 west flowing major rivers. It is now identified that these pristine habitats are unique biological regions and ‘hotspots' of fish diversity. The river systems consist of mainly the running water habitat and lacustrine habitats. There are numerous small lakes and ponds throughout the Western Ghats, which form the standing water habitats. Apart from these, there are forest swamps, deep wells, estuaries, gorges, etc, which are responsible for diverse fish fauna of the region.

A running water stream habitat

A stream with rich riparian vegetation on both sides

Estuaries are the meeting places of both freshwater and marine forms of fishes

Lacustrine habitats that are formed due to the construction of dams across the rivers

Stream with cascading type of habitat

Torrential streams are the special features of Western Ghats

Stream headwaters are the regions of specially adapted hillstream fishes

Gradually flowing river in Coastal region

Lake habitats in the Western Ghats

It can be observed that the species composition in these different habitats differs significantly between each other. Hill-streams dominate with the species of Balitoridae, especially the species of the genus Schistura. The torrential habitats compose of the highly adapted species of Garra, Glypththorax, etc. Shallow gradually flowing streams are rich with most general and small species (Ex. Puntius, Danio, Rasbora, Aplocheilus, etc). Species composition in the lacustrine habitats is mainly influenced by human beings in terms of exotic species introduction and large-scale harvesting. In these types of habitats large and medium commercial fishes dominate along with native commercial fishes. The exotic fish in the Western Ghats are Cyprinus carpio, Carassius carassius, Tinca tinca, Oreochromis mossambicus and the rainbow trout Oncorhynchus mykiss (golden and ordinary strains). The estuaries are dominated with dadromous and secondary freshwater fishes. Some of the Wells in Kerala are recorded with the blind catfishes such as Horaglanis krishnai and H. alikunhi.

The freshwater ecosystems of the Western Ghats are characterized by their patchy nature. Due to which each freshwater ecosystem, say a river or lake can be considered as an island with its own environmental characteristics. This situation might have allowed to occur allopatric speciation and several species are known only from a drainage or a portion of the drainage system. This could be one of the important reasons behind, the exceptional fish diversity in Western Ghats and yet so endemic and threatened.

Connection between river basins

Natural inter-basin transfer of fish fauna takes place when the terrain is flat and receives heavy rainfall that inundates the entire region. In case of Western Ghats, although rainfall is of the range of 6000mm annually, undulating terrain and great slopes of the basin provides little scope for inter-basin transfer of the fish fauna. However, recent anthropogenic activities in the form of damming the rivers and inter-basin transfer of water are the possible pathway for fish fauna to exchange between river basins.

Coastal connections

These are the connections available for diadromous and estuarine fishes to move from one basin to another, during monsoon season, when large amount of freshwater enters the sea from the estuary. Fishes that can withstand the reduced salinity of the sea possibly migrate to the nearest basin and recolonise.

Falls as barriers to fish migration

Within a river basin, presence of falls greatly hinders the upstream and downstream movement of fishes. Most of the west-flowing rivers in the Western Ghats originate at the hilltop and after covering certain distance, they leap down over a great depth, forming natural falls. A study carried out by Bhat (2003) in four west flowing rivers of the Western Ghats of Karnataka found that upper reaches of the falls between the rivers were more similar to each other than comparing upper and lower reaches on the same river.

THREATS TO FRESHWATER BIODIVERSITY WITH SPECIAL REFERENCE TO WESTERN GHATS REGION

The Western Ghats region, like other parts of the tropics, is undergoing rapid transformation. The deforestation rate is high and forests are being transformed into agriculture and monoculture plantations. Hydroelectric projects, mining, and extraction of forest products are also altering the landscape (Bawa and Menon, 1997). Major human induced ecological changes in the Western Ghats begin with the arrival of agriculture and pastoralism. A climatic change towards the middle of fourth millennium BP, which induced widespread human migrations within the Indian sub-continent, is correlated to decline of forests and mangroves in Western Ghats. The ecosystems in the Western Ghats do bear the imprints of human actions through history (Chandran, 1997).

Habitat fragmentation

Fragmentation, the loss and isolation of natural habitats, is one of the greatest threats to regional and global biodiversity. Habitat fragmentation takes place when the continuity is broken. This may be mainly through the construction of dams across the rivers, conversion of wetlands into other forms of land uses, destruction of riparian vegetation, etc. Eight kinds of species have been identified that are likely to be especially vulnerable to the effects of fragmentation: rare species, species with large home ranges, species with limited powers of dispersal, species with low reproductive potential, species with short life cycles, species dependent on resources that are unpredictable in time or space, species of habitat interiors, and species exploited or persecuted by people. Due to the terrain of the Western Ghats, the rivers are extensively harvested for hydroelectric power through the construction of dams resulting in the fragmentation of the rivers. Anadromous fishes begin their life in freshwater, move to the marine environment to grow and mature, and then return to freshwater to reproduce. In Western Ghats decline in the population of Anguilla bengalensis has been attributed to fragmented rivers.

Land use change in the catchment

The cumulative geographical, hydrological, and ecological impacts of deforestation, timber harvesting, destruction of riparian vegetation, agricultural development, urbanization, land drainage, and flood protection on rivers have been documented worldwide. Deforestation of the catchment area usually results in soil erosion and nutrient input into the rivers. Destruction of riparian vegetation damages the coarse stream substrate where several fishes find their shelter. High suspended sediment concentrations in rivers and sediment deposition on the riverbed can affect the health, habitat and particularly damage the gills. It has been estimated that about 25.6 % of the forest cover in Western Ghats is lost over a span of 22 years.

The Western Ghats region is prone to large-scale mining activities. These activities contribute huge quantities of silt into the aquatic systems. The rapid transformation of habitats in the form of silt deposition may result in the total changes in the species composition of the particular habitat.

Flow regulation

Flow regulation is mainly due to the construction of dams across the rivers. It can be estimated that more than 60 % of the worlds is and many rivers have reduced to cascades of manmade lakes. This clearly reveals the magnitude of flow regulations all over the world. The flow regulation removes the lotic habitats and give rise to lentic habitats. Also, the homogenization of the habitats and within which it forms the temperature gradients.

Interlinking of river basins

The concept of interlinking of river basins is gaining importance in recent years. Several such schemes in India and abroad have already being commissioned. However the serious repercussions in terms of water balance, water quality, the spread of pests and diseases, alterations to natural biotic distribution patterns and the disruption of significant ecological processes. In Indian context, the Western Ghats are characterised by high levels of fish endemism and the Himalayan region in terms of high diversity. Interlinking of the rivers of India may disrupt the distribution patterns of the fishes. Some fishes may find new optimal habitats and flourish prolifically on the expense of other native fishes. Possibly the native fishes may be rare and endemic fishes needing immediate conservation measures. Thus in the process several species may become extinct and several may flourish. The concept of interlinking of the rivers of India is in the process of implementation. In this connection the above-discussed possibilities may be quite relevant to be considered.

Over harvesting destructive fishing methods

Fishes are regarded as the rich sources of protein. Throughout the world, fishing has offered employment to thousands of families. Subsistence fishing in streams, rivers and tanks has been a source of living for weaker section of the society. All these aspects have resulted in commercialization of fishery. The annual commercial catch from the fisheries of the world is approaching 100 million t. Such a tremendous rate of extraction from the aquatic ecosystem has adversely affected the fish base of the world. Human uses of freshwater resources have threatened the sustainability of these resources. Increase in the fishing population and the demand for fish has intensified the fishing activities. Fishermen are using the destructive methods of fishing to get higher yields. Illegal usage of small meshed fishing gears that damage the juveniles, is still in use. Fishing using chemical and herbal poisons like copper sulphate, bleaching powder, tree extracts damage the entire fish population of the aquatic body. Dynamiting is another destructive method by which fishermen easily collect huge quantity of fishes. Use of dragnets which sweep away the entire fish resource of a particular area including juveniles can be disastrous to both target and non-target fishes of the area.

Introduction of alien species

A number of species get introduced into the waters, most of which are to the reservoir areas of dams with a view to increase the net fish yield of the reservoir. Of these introduced fishes, many have naturalised in the streams, ponds and tanks of the region. Species like Oreochromis mossambica, Gambusia offinis, Poecilia reticulata, etc. are exotic species, which are originally from Africa and South America and introduced extensively in India. Species like Labeo rohita, Catla catla, Cirhinus mrigala have been introduced recently in to the reservoirs. Importantly Cyprinus carpio has been widely introduced into the reservoirs of Western Ghats. This kind of haphazard introduction not only jeopardized the reservoirs but also threatened the freshwater biodiversity.

Chemical and thermal pollution

Changes in water quality due to discharge of effluents from various industrial, domestic and agricultural sources have deteriorated water quality. The toxic elements in pollutants may be total, killing all the fish species present, or selective, destroying a few sensitive species or so altering the environment that some species are favoured and others not.

Diseases

Several incidences of outbreak of the diseases such as EUS (Epizootic Ulcerative syndrome) have been witnessed in freshwater habitats of Western Ghats. These have affected the sensitive native fishes of the region. For instance, in the last decade, large-scale mortality of freshwater fish took place due to EUS in most parts of the Western Ghats and the country as well.

Conservation practices of freshwater fishes in Western Ghats region

Roughly 318 species of fish, which have been identified, are undoubtedly the relics of the several hundreds of species that have ever existed in this region. The reason behind existence of these modern survivors may be presence of some of the excellent basins in good condition within the region and traditional conservation practices in terms of protected sites, temple ponds, etc. The traditional practices involve declaring a stretch of river or a pond as sacred and giving the fullest protection to the fishes dwelling in them. However, to conserve the existing fish resources of the region, several other management strategies need to be designed and implemented.

Properly maintained scientific data on the fish fauna of the water body, participatory approaches in conservation, educating the fishing communities, managing the terrestrial ecosystem in healthy condition, stopping the introduction of exotic species, and careful extraction, in situ and ex situ conservation practices for the critically endangered species, etc. can be listed. However, the basic requisite is the change of view about the Western Ghats from a region of production to a region of conservation.

References and Books

Annexure Top

*Checklist of freshwater fishes of Western Ghats (Compiled from various published sources)
Note : CR - Critically Endangered, EN - Endangered, VU - Vulnerable, LR - Lower Risk, DD - Data Deficient.

Endemic Species of Western Ghats

S.No.
Species Name
Status
S.No.
Species Name
Status
1

Amblypharyngodon chakaiensis

CR

69

Monopterus eapeni

CR

2

Balitora brucei

DD

70

Mystus malabaricus

EN

3

Balitora mysorensis

CR

71

Mystus punctatus

EN

4

Barilius bakeri

VU

72

Nemacheilichthys ruppelli

DD

5

Barilius canarensis

DD

73

Nemacheilus anguilla

LR

6

Barilius evezardii

LR

74

Nemacheilus keralensis

EN

7

Barilius gatensis

DD

75

Nemacheilus monilis

EN

8

Batasio sharavatiensis

DD

76

Nemacheilus pambarensis

DD

9

Batasio travancoria

EN

77

Neolissochilus wynaadensis

CR

10

Bhavania australis

EN

78

Ompok malabaricus

CR

11

Botia striata

EN

79

Osteobrama bakeri

EN

12

Chela dadyburjori

DD

80

Osteobrama bheemensis

DD

13

Chela fasciata

CR

81

Osteobrama neilli

DD

14

Clarias dayi

EN

82

Osteocheilichthys longidorsalis

CR

15

Crossocheilus periyarensis

VU

83

Osteocheilichthys nashii

VU

16

Danio fraseri

DD

84

Osteocheilichthys thomassi

EN

17

Dayella malabarica

LR

85

Osteochilichthys godavariensis

DD

18

Esomus barbatus

DD

86

Osteochilus (Kantaka) brevidorsalis

EN

19

Etroplus suratensis

LR

87

Pangio bashai

DD

20

Eutropiichthys goongwaree

DD

88

Parambassis dayi

EN

21

Garra bicornuta

DD

89

Parapsilorhynchus discofhorus

DD

22

Garra gotyla stenorhynchus

EN

90

Parapsilorhynchus prateri

DD

23

Garra hughi

EN

91

Parmabassis thomassi

VU

24

Garra kalakadensis

DD

92

Pristolepis marginata

VU

25

Garra mcclellandi

EN

93

Pseudeutropius mitchelli

DD

26

Garra menoni

VU

94

Puntius arenatus

DD

27

Garra surendranathanii

LR

95

Puntius arulius arulius

EN

28

Glypthothorax conirostre poonaensis

DD

96

Puntius arulius tambraparniei

CR

29

Glyptothorax anamalaiensis

CR

97

Puntius bovanicus

CR

30

Glyptothorax devisinghi

CR

98

Puntius carnaticus

VU

31

Glyptothorax housei

DD

99

Puntius cauveriensis

DD

32

Glyptothorax lonah

LR

100

Puntius chalakudaiensis

DD

33

Glyptothorax madraspatanum

VU

101

Puntius crescentus

DD

34

Glyptothorax trewavasae

DD

102

Puntius deccanensis

CR

35

Gonoproktopterus curmuca

EN

103

Puntius denisonii

EN

36

Gonoproktopterus dubius

EN

104

Puntius fraseri

DD

37

Gonoproktopterus kolus

EN

105

Puntius goaensis

EN

38

Gonoproktopterus kurali

EN

106

Puntius jerdoni

EN

39

Gonoproktopterus lithopidos

EN

107

Puntius kannikattiensis

DD

40

Gonoproktopterus micropogon

EN

108

Puntius melanostigma

EN

41

Gonoproktopterus thomassi

EN

109

Puntius mudumalaiensis

CR

42

Heteropneustes longipectoralis

DD

110

Puntius narayani

CR

43

Homaloptera menoni

DD

111

Puntius ophicephalus

EN

44

Homaloptera montana

CR

112

Puntius parrah

EN

45

Homaloptera pillaii

VU

113

Puntius sahyadriensis

DD

46

Homaloptera santhampareiensis

DD

114

Puntius sarana subnasutus

LR

47

Horabagrus brachysoma

EN

115

Puntius setnai

DD

48

Horabagrus nigricollaris

CR

116

Puntius sharmai

DD

49

Horaglanis alikunhi

DD

117

Rasbora caverii

DD

50

Horaglanis krishnai

CR

118

Rasbora labiosa

DD

51

Horalabiosa joshuai

DD

119

Rohtee ogilbii

LR

52

Horalabiosa palaniensis

DD

120

Salmostoma boopis

LR

53

Hyporhampus xanthopterus

CR

121

Salmostoma horai

DD

54

Labeo ariza

CR

122

Salmostoma novacula

LR

55

Labeo dussumieri

EN

123

Schismatorhynchus (Nukta) nukta

DD

56

Labeo kontius

EN

124

Schistura denisoni mukambbikaensis

DD

57

Labeo nigrescens

DD

125

Schistura denisoni pambarensis

DD

58

Labeo potail

DD

126

Schistura kodaguensis

DD

59

Lepidopygopsis typus

CR

127

Schistura nilgiriensis

EN

60

Longischistura striatus

DD

128

Schistura semiarmatus

VU

61

Macropodus dayi

DD

129

Schistura sinuatus

DD

62

Mesonemacheilus guentheri

LR

130

Silonia childreni

EN

63

Mesonemacheilus herrei

DD

131

Silurus wynaadensis

CR

64

Mesonemacheilus petrubanarescui

DD

132

Tetraodon travancoricus

EN

65

Mesonemacheilus pulchellus

DD

133

Tor khudree malabaricus

CR

66

Mesonemacheilus triangularis

LR

134

Tor mussulah

CR

67

Monopterus (Amphipnous) fossorius

EN

135

Travancoria jonesi

EN

68

Monopterus (Amphipnous) indicus

DD

136

Travencoria elongata

CR

Non-endemic Species of Western Ghats

S.No.
Species Name
Status
S.No.
Species Name
Status
1

Acanthocobitis botia

LR

89

Mastacembelus armatus

LR

2

Acanthocobitis moreh

DD

90

Megalops cyprinoides

DD

3

Ambassis gymnocephalus

DD

91

Microphis cuncalus

VU

4

Ambassis interruptus

DD

92

Mugil cephalus

DD

5

Ambassis nalua

DD

93

Mystus armatus

LR

6

Amblypharyngodon melettinus

LR

94

Mystus bleekeri

VU

7

Amblypharyngodon microlepis

DD

95

Mystus cavesius

LR

8

Amblypharyngodon mola

LR

96

Mystus gulio

LR

9

Anabas testudineus

VU

97

Mystus keletius

DD

10

Anguilla bengalensis bengalensis

EN

98

Mystus menoda

DD

11

Anguilla bicolor bicolor

EN

99

Mystus montanus

VU

12

Aphanius dispar

DD

100

Mystus oculatus

LR

13

Aplocheilus blocki

DD

101

Mystus viittatus

VU

14

Aplocheilus lineatus

LR

102

Nandus nandus

LR

15

Aplocheilus panchax

DD

103

Nangra itchkeea

DD

16

Aspidoparia morar

LR

104

Nemacheilus beavani

DD

17

Awaous grammepomus

DD

105

Nemacheilus viridescens

LR

18

Awaous gutum

DD

106

Neotropius khavalchor

DD

19

Badis badis

DD

107

Notopterus chitala

EN

20

Bagarichthys yarrellii

DD

108

Notopterus notopterus

LR

21

Bagarius bagarius

VU

109

Omobranchus punctatus

DD

22

Balitora brucei

LR

110

Omobranchus zebra

DD

23

Barilius barila

VU

111

Ompok bimaculatus

EN

24

Barilius barna

LR

112

Ompok pabo

DD

25

Barilius bendelisis

LR

113

Oreichthys cosuatis

DD

26

Barilius vagra

VU

114

Oreonectes evezardi

EN

27

Bathygobius fuscus

DD

115

Oryzias melastigma

DD

28

Brachydanio rerio

LR

116

Osphronemus goramy

DD

29

Brachygobius nunus

DD

117

Osteobrama belangeri

EN

30

Catla catla

VU

118

Osteobrama cotio cotio

LR

31

Chanda nama

VU

119

Osteobrama cotio cunma

VU

32

Channa marulius

LR

120

Osteobrama cotio peninsularis

EN

33

Channa micropeltes

CR

121

Osteobrama vigorsii

DD

34

Channa orientalis

VU

122

Pangasius pangasius

CR

35

Channa punctatus

LR

123

Parambassis ranga

DD

36

Channa striatus

LR

124

Parapsilorhynchus tentaculatus

DD

37

Chela cachius

DD

125

Periophthalmus variabilis

DD

38

Chela laubuca

LR

126

Pomadasys argenteus

DD

39

Chelonodon patoca

DD

127

Pristolepis fasciata

DD

40

Cirhinus fulungee

LR

128

Proeutropiichthys taakree taakree

CR

41

Cirhinus mrigala mrigala

LR

129

Pseudambassis baculis

DD

42

Cirhinus reba

VU

130

Pseudeutropius atherinoides

EN

43

Cirrhinus cirrhosus

VU

131

Puntius amphibius

LR

44

Clarias batrachus

VU

132

Puntius bimaculatus

DD

45

Clarias dussumieri dussumieri

VU

133

Puntius burmanicus

DD

46

Crossocheilus latius latius

DD

134

Puntius chola

VU

47

Danio aequipinatus

LR

135

Puntius conchonius

VU

48

Danio malabaricus

LR

136

Puntius dorsalis

EN

49

Danio neilgherriensis

DD

137

Puntius fasciatus fasciatus

EN

50

Esomus danricas

VU

138

Puntius filamentosus

DD

51

Esomus thermoicos

DD

139

Puntius guganio

LR

52

Etroplus canarensis

DD

140

Puntius phutunio

LR

53

Etroplus maculatus

LR

141

Puntius pleurotaenia

VU

54

Euryglossa orientalis

DD

142

Puntius sarana orphoides

DD

55

Eutropichthys vacha

EN

143

Puntius sarana sarana

VU

56

Gagata gagata

DD

144

Puntius sophore

LR

57

Garra gotyla gotyla

VU

145

Puntius ticto ticto

LR

58

Garra lamta

DD

146

Puntius vittatus

VU

59

Garra mullya

LR

147

Rasbora daniconius

LR

60

Glossogobius giuris

LR

148

Rasbora rasbora

DD

61

Glyptothorax annandalei

EN

149

Rhinomugil corsula

VU

62

Glyptothorax saisii

EN

150

Rita kuturnee

LR

63

Heteropneustes fossilis

VU

151

Rita pavimentatus

EN

64

Hilsa ilisha

VU

152

Rita rita

LR

65

Hilsha kelee

DD

153

Salmo gardineri

DD

66

Horaichthys setnai

DD

154

Salmostoma acinaces

VU

67

Hyporhamphus limbatus

DD

155

Salmostoma bacaila

LR

68

Ichthyocampus carce

DD

156

Salmostoma clupeoides

EN

69

Johnius belangerii

DD

157

Salmostoma phulo

DD

70

Labeo bata

LR

158

Scatophagus argus

DD

71

Labeo boga

LR

159

Schistura denisoni denisoni

VU

72

Labeo boggut

DD

160

Schistura savona

DD

73

Labeo calbasu

LR

161

Schistura denisoni dayi

DD

74

Labeo fimbriatus

LR

162

Sicyopterus fasciatum

DD

75

Labeo gonius

LR

163

Silurus berdmorei

DD

76

Labeo kawrus

DD

164

Sperata aor

DD

77

Labeo pangusia

LR

165

Sperata seenghala

DD

78

Labeo porcellus

DD

166

Stigmatogobius javanicus

DD

79

Labeo rohita

LR

167

Stigmatogobius sadanundio

DD

80

Labeo sindensis

DD

168

Strongylura strongylura

DD

81

Lepidocephalus guntea

DD

169

Syciopterus griseus

VU

82

Lepidocephalus thermalis

LR

170

Tor khudree

VU

83

Liza macrolepis

DD

171

Tor mosal

EN

84

Liza parsia

DD

172

Tor putitora

EN

85

Lutjanus johni

DD

173

Tor tor

EN

86

Macrognathus guentheri

VU

174

Wallago attu

LR

87

Macrognathus pancalus

LR

175

Xenentodon cancila

LR

88

Macropodus cupanus

DD

176

Zenarchopterus striga

DD

Introduced Species

S.No.
Species Name
1

Ctenopharyngodon idella

2

Cyprinus carpio communis

3

Gambusia affinis

4

Oreochromis mossambica

5

Poecilia (Lebistes) reticulata

6

Xiphophorus helleri