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Crustacean Community in Anchar lake, Kashmir
I. A. Ahangar1,D. N. Saksena1, M. Farooq Mir2 andM. Afzal Ahangar3
1School of Studies in Zoology, Jiwaji University, Gwalior (M.P) India-474011.
2Hydrobiology Research Laboratory, Govt. S.P College, Srinagar.
3Department of Zoology, Govt. S.P College, Srinagar.
Corresponding Author: ahangarzoo@gmail.com
ABSTRACT
The paper deals with the species composition and population dynamics of Crustacea in Anchar lake of Kashmir under the
influence of certain environmental factors. The Crustacean fauna was represented by eleven species. The group showed
maximum numerical surge during warm periods and minimum in colder periods. The species diversity was composed of
Daphnidae followed by Bosminidae, Moinidae and Macrothricidae in decreasing order. The population dynamics was mainly
influenced by water level fluctuations and macrophytic density.
Key words: Anchar Lake, Cladocera, Crustacea and Kashmir
INTRODUCTION
The importance of Crustacea in the trophic dynamics of freshwater ecosystems has long been
recognized. They are the consumers of first order, directly drawing energy from primary producers
of the ecosystem, viz., phytoplankton and in turn form the food of a large number of planktivorous
fishes , other invertebrates and thereby help in transferring energy to the higher trophic levels.
Because of varied response to ecological features by different species, many of them act as reliable
indicators of the trophic status of water bodies. A detailed limnological study of Anchar Lake
(Kashmir) was conducted during June 2010 to May 2011 and the study is based on a part of the data
collected during this study and describes the diversity and distribution pattern of Crustacea in
response to environmental characteristics in this wetland.
STUDY SITES
Anchar lake is a shallow basined lake with fluviatile origin, situated near Soura 12 km to the north
west of Srinagar city at an altitude of 1583 m.s.l and lies within the geographical coordinates of 34⁰
20΄- 34⁰ 36΄N latitude and 74⁰82΄ - 74⁰ 85΄E longitudes in a semi urban conditions. The site I is
situated almost in the centre of the lake in the open water area with a maximum depth of 1.73 m and
with little submerged vegetation growth. Site-II lies near the outlet of the lake towards the Sangam
village lying in the west. The site has a maximum water depth of 1.23 m. Site- III is slightly away
from the site II with maximum water depth of 1.72 m. The site is near the inlet of river Sind into the
lake and the vegetation is dominated by Phragmites australis, Typha angustata and Sparganium
erectum. Site–IV has been selected towards the eastern side of the lake near SKIMS Hospital. The site
has maximum water depth of 1.66 m and is recognized by the vigorous growth of pollution indicator
species like Myriophyllum verticillatum, Hydrocharis dubia and Potamogeton natans. Small but
stretched patches of lotus (Nelumbo nucifera) are separated by these networks of channels.
Dominant forms of Macrophytes in the wetland include: Ceratophyllum demersum, Myriophyllum
spicatum, M. verticillatum, Nymphea spp., Potamogeton spp., Polygonum spp., Sparganium erectum,
Nymphoides peliata, Utricularia flexuosa, Typha angustata and Phragmites australis.
MATERIALS AND METHODS
Qualitative and Quantitative samples of Crustacea were collected on monthly basis with the help of
plankton net and were preserved in 4% formalin. Detailed taxonomic identification was carried out
following [1], [2], [3], [4] and [5]
Original Article
Bulletin of Environment, Pharmacology and Life Sciences
Online ISSN 2277 – 1808
Bull. Environ. Pharmacol. Life Sci.; Volume 1 [7] June 2012: 18 - 21
© All Rights Reserved Academy for Environment and Life Sciences, India
Website: www.bepls.com
- 19 -
RESULTS AND DISCUSSION
Biological features
Different species of Crustacea were recorded from Anchar Lake (Table 1). Of these two belong to
Bosminidae, two to Daphnidae, one each to Moinidae, Macrothricidae and Chydoridae. Species
number was highest at site II and site III followed closely by site IV and site I. The peak population
was observed in August and lowest population in colder periods (Fig 1). Almost similar results have
been obtained by [6] in Manasbal Lake. The maximum population of crustaceans occurred in
summer and spring time when temperature, dissolved oxygen were conducive and the food source
in the form of phytoplankton and microbial organic matter was in abundance [7] [8]. A comparison
of different families revealed that highest population density recorded follows sequence Daphnidae >
Bosminidae > Chydoridae > Moinidae > Macrothicidae > Cypridae in decreasing order. The highest
population density recorded seems to be related with the diverse macrophytic community
sustaining rich periphytic algal growth at the different sites [9] [10] [11] [12] [13]. An analysis of the
composition of the population of different families revealed that Daphnidae, Cyclopoidae and
Bosminidae were the dominant components (79%), (73%) and (51%) respectively at site II.
Dominance of Chydoridae, Bosminidae and Daphnidae seems to be related to the eutrophic nature of
the water [14] [15]. On the whole sequence of dominance amoung the cladoceran groups in the
wetland was:
Daphnidae > Cyclopoidae > Bosminidae > Macrothicidae > Moinidae > Cypridae
The lake is readily divisible into two distinct areas, i.e, (i) area with sparse vegetation (site I and site
II) and (ii) area having dense macrophytic vegetation (site III and site IV). Most of the crustacean
species recorded from the lake was common in both the areas as they are free swimming forms and
have better locomotory power than Rotifers [1] and only few species are restricted to the sparsely
vegetated areas. Moina brachiata, Cypris subglobosa, Bosmina coregoni, Bosmina longirostris and
Cyclops scutifera were absent at sites II, III, and I respectively. However the most dominant forms in
the lake were Daphnia magna, Daphnia pulex, Chydorous sphaericus, Bosmina longirostris, Macrothrix
rosea and Cyclops bicuspidatus. All these are true representatives of shallow eutrophic habitats and
were widely distributed in the lake almost throughout the year. Others were only seasonal in their
occurrence.
According to [3] crustacean plankton in a freshwater habitat at a particular moment is generally
composed by one dominant species, one or two sub dominant species and the remaining species
make up only the small fraction of the whole population. The present data do not support this view.
This is probably due to the fact that the shallow nature of the lake supports a rich population of
macrophytic community, which in turn provides varied microhabitats for the different animal
associations including Cladocera. It may be concluded that the Crustacean fauna of the wetland is
characterized by typical littoral Crustacean community mainly influenced by the fluctuations in the
water level and the macrophytic density.
List of Crustacean species observed in Anchar Lake
 Family: CLADOCERA
 Alona affinis
 Bosmina longirostris
 Bosmina coregoni
 Daphnia magna
 Daphnia pulex
 Moina brachiata
 Chydorous sphaericus
 Macrothrix rosea
 Family: COPEPODA
 Cyclops scutifera
 Cyclops bicuspidatus
 Family: OSTRACODA
 Cypris subglobosa
Ahangar et al
- 20 -
Fig 1: Monthly fluctuations in the population of Crustacea in Anchar Lake
.
Fig 2: Percentage composition of different families of Crustacea in Anchar Lake
Table 1: List of species family wise recorded in Anchar lake.
Family: Bosminidae
 Bosmina longirostris
 Bosmina coregoni
Family: Daphnidae
 Daphnia magna
 Daphnia pulex
Family: Macrothricidae
 Macrothrix rosea
Family: Chydoridae
 Chydorous sphaericus
Family: Moinidae
 Moina brachiata
Family: Cyclopoida
 Cyclops scutifera
 Cyclops bicuspidatus
Family: Cypridae
 Cypris subglobosa
Fig 3 : Dominance pattern of different Crustacean families in Anchar lake.
Ahangar et al
- 21 -
CONCLUSION
The maximum population of crustacea occurred in summer and spring time when temperature,
dissolved oxygen were conducive and the food source in the form of phytoplankton and microbial
organic matter was in abundance. Most of the crustacean species recorded from the lake was
common in both the areas as they are free swimming forms and have better locomotory power than
Rotifers.
ACKNOWLEDGEMENTS
The authors are highly thankful to the Senior Research Scholars of Aquatic Biology Laboratory,
School of Studies in Zoology, Jiwaji University, Gwalior and Hydrobiology Research Laboratory,
Govt. S. P. College, Srinagar for their valuable guidance and timely help.
REFERENCES
1. Edmondson, W. T., (1959). Ward and Whipple’s Freshwater Biology, 2nd Ed. John Wiley and Sons, INC. New York.
2. A. P. H. A. (1998). Standard Methods for Examination of water and wastewater. 20th Ed. American Public Health
Association, Washington, D.C.
3. Pennak, R.W. (1957). Species composition of limnetic zooplankton communities. Limnol.Oceanogr. 2(3): 222-223.
4. Battish, S. K. (1992). Freshwater zooplankton of India. Oxford and IBH publications, New Delhi.
5. Adoni, A. D. (1985). Workbook of Limnology. Pratibha Publications, Sagar.
6. Yousuf, A. R. (1989). Zooplankton studies in India with special references to North India. A critical review.
Management of Aquatic Ecosystem. P. 309-324.
7. Schmitz, D. C. and Osborne, J. A. (1984). Zooplankton densities in a Hydrilla infested lake. Hydrobol. 111:127-132.
8. Beaver, J. R., Lemke, A. M. and Acton, J. K. (1999). Midsummer zooplankton assemblages in four types of wetlands in
the upper Midwest, USA. Hydrobiol. 308: 209-220.
9. Smyly, W. J. P., (1958). Distribution and seasonal abundance of Entomostraca in Moorland ponds near Windermere.
Hydrobiol. 11: 59-72.
10. Straskraba, M. (1965). Quantitative study of the littoral zooplankton of the rich vegetation of the backwater Labicko.
Hydrobiol. 26:421-433.
11. Cowell, B. C., Dyne, C. W. and Adama, R. C. (1975). A synoptic study of the limnology of lake Thonotosassa, Florida.
Effects of primary treated sewage and citrus wastes.
12. Nordlie, R. G. (1976). Plankton communities of three Central Florida lakes. Hydrobiol.48:65-78.
13. Pandit, A. K. (1980). Biotic Factor and Food Chain Structure in Some Typical Wetlands of Kashmir. Ph. D. Thesis,
University of Kashmir, Srinagar-6, J&K.
14. Das, S. M. (1956). A Quantitative studies on fluctuations of plankton in two Kumaon lakes, Nainital and Bhimtal (India).
Acta. Hydrobiol., 2(1): 9-17.
15. Balkhi, S. M. H. and Yousuf, A. R. (1992). Community structure of crustacean plankton in relation to trophic conditions.
Int. J. Ecol. & Env. Sci. 18:155-168.
Ahangar et al

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4

  • 1. - 18 - Crustacean Community in Anchar lake, Kashmir I. A. Ahangar1,D. N. Saksena1, M. Farooq Mir2 andM. Afzal Ahangar3 1School of Studies in Zoology, Jiwaji University, Gwalior (M.P) India-474011. 2Hydrobiology Research Laboratory, Govt. S.P College, Srinagar. 3Department of Zoology, Govt. S.P College, Srinagar. Corresponding Author: ahangarzoo@gmail.com ABSTRACT The paper deals with the species composition and population dynamics of Crustacea in Anchar lake of Kashmir under the influence of certain environmental factors. The Crustacean fauna was represented by eleven species. The group showed maximum numerical surge during warm periods and minimum in colder periods. The species diversity was composed of Daphnidae followed by Bosminidae, Moinidae and Macrothricidae in decreasing order. The population dynamics was mainly influenced by water level fluctuations and macrophytic density. Key words: Anchar Lake, Cladocera, Crustacea and Kashmir INTRODUCTION The importance of Crustacea in the trophic dynamics of freshwater ecosystems has long been recognized. They are the consumers of first order, directly drawing energy from primary producers of the ecosystem, viz., phytoplankton and in turn form the food of a large number of planktivorous fishes , other invertebrates and thereby help in transferring energy to the higher trophic levels. Because of varied response to ecological features by different species, many of them act as reliable indicators of the trophic status of water bodies. A detailed limnological study of Anchar Lake (Kashmir) was conducted during June 2010 to May 2011 and the study is based on a part of the data collected during this study and describes the diversity and distribution pattern of Crustacea in response to environmental characteristics in this wetland. STUDY SITES Anchar lake is a shallow basined lake with fluviatile origin, situated near Soura 12 km to the north west of Srinagar city at an altitude of 1583 m.s.l and lies within the geographical coordinates of 34⁰ 20΄- 34⁰ 36΄N latitude and 74⁰82΄ - 74⁰ 85΄E longitudes in a semi urban conditions. The site I is situated almost in the centre of the lake in the open water area with a maximum depth of 1.73 m and with little submerged vegetation growth. Site-II lies near the outlet of the lake towards the Sangam village lying in the west. The site has a maximum water depth of 1.23 m. Site- III is slightly away from the site II with maximum water depth of 1.72 m. The site is near the inlet of river Sind into the lake and the vegetation is dominated by Phragmites australis, Typha angustata and Sparganium erectum. Site–IV has been selected towards the eastern side of the lake near SKIMS Hospital. The site has maximum water depth of 1.66 m and is recognized by the vigorous growth of pollution indicator species like Myriophyllum verticillatum, Hydrocharis dubia and Potamogeton natans. Small but stretched patches of lotus (Nelumbo nucifera) are separated by these networks of channels. Dominant forms of Macrophytes in the wetland include: Ceratophyllum demersum, Myriophyllum spicatum, M. verticillatum, Nymphea spp., Potamogeton spp., Polygonum spp., Sparganium erectum, Nymphoides peliata, Utricularia flexuosa, Typha angustata and Phragmites australis. MATERIALS AND METHODS Qualitative and Quantitative samples of Crustacea were collected on monthly basis with the help of plankton net and were preserved in 4% formalin. Detailed taxonomic identification was carried out following [1], [2], [3], [4] and [5] Original Article Bulletin of Environment, Pharmacology and Life Sciences Online ISSN 2277 – 1808 Bull. Environ. Pharmacol. Life Sci.; Volume 1 [7] June 2012: 18 - 21 © All Rights Reserved Academy for Environment and Life Sciences, India Website: www.bepls.com
  • 2. - 19 - RESULTS AND DISCUSSION Biological features Different species of Crustacea were recorded from Anchar Lake (Table 1). Of these two belong to Bosminidae, two to Daphnidae, one each to Moinidae, Macrothricidae and Chydoridae. Species number was highest at site II and site III followed closely by site IV and site I. The peak population was observed in August and lowest population in colder periods (Fig 1). Almost similar results have been obtained by [6] in Manasbal Lake. The maximum population of crustaceans occurred in summer and spring time when temperature, dissolved oxygen were conducive and the food source in the form of phytoplankton and microbial organic matter was in abundance [7] [8]. A comparison of different families revealed that highest population density recorded follows sequence Daphnidae > Bosminidae > Chydoridae > Moinidae > Macrothicidae > Cypridae in decreasing order. The highest population density recorded seems to be related with the diverse macrophytic community sustaining rich periphytic algal growth at the different sites [9] [10] [11] [12] [13]. An analysis of the composition of the population of different families revealed that Daphnidae, Cyclopoidae and Bosminidae were the dominant components (79%), (73%) and (51%) respectively at site II. Dominance of Chydoridae, Bosminidae and Daphnidae seems to be related to the eutrophic nature of the water [14] [15]. On the whole sequence of dominance amoung the cladoceran groups in the wetland was: Daphnidae > Cyclopoidae > Bosminidae > Macrothicidae > Moinidae > Cypridae The lake is readily divisible into two distinct areas, i.e, (i) area with sparse vegetation (site I and site II) and (ii) area having dense macrophytic vegetation (site III and site IV). Most of the crustacean species recorded from the lake was common in both the areas as they are free swimming forms and have better locomotory power than Rotifers [1] and only few species are restricted to the sparsely vegetated areas. Moina brachiata, Cypris subglobosa, Bosmina coregoni, Bosmina longirostris and Cyclops scutifera were absent at sites II, III, and I respectively. However the most dominant forms in the lake were Daphnia magna, Daphnia pulex, Chydorous sphaericus, Bosmina longirostris, Macrothrix rosea and Cyclops bicuspidatus. All these are true representatives of shallow eutrophic habitats and were widely distributed in the lake almost throughout the year. Others were only seasonal in their occurrence. According to [3] crustacean plankton in a freshwater habitat at a particular moment is generally composed by one dominant species, one or two sub dominant species and the remaining species make up only the small fraction of the whole population. The present data do not support this view. This is probably due to the fact that the shallow nature of the lake supports a rich population of macrophytic community, which in turn provides varied microhabitats for the different animal associations including Cladocera. It may be concluded that the Crustacean fauna of the wetland is characterized by typical littoral Crustacean community mainly influenced by the fluctuations in the water level and the macrophytic density. List of Crustacean species observed in Anchar Lake  Family: CLADOCERA  Alona affinis  Bosmina longirostris  Bosmina coregoni  Daphnia magna  Daphnia pulex  Moina brachiata  Chydorous sphaericus  Macrothrix rosea  Family: COPEPODA  Cyclops scutifera  Cyclops bicuspidatus  Family: OSTRACODA  Cypris subglobosa Ahangar et al
  • 3. - 20 - Fig 1: Monthly fluctuations in the population of Crustacea in Anchar Lake . Fig 2: Percentage composition of different families of Crustacea in Anchar Lake Table 1: List of species family wise recorded in Anchar lake. Family: Bosminidae  Bosmina longirostris  Bosmina coregoni Family: Daphnidae  Daphnia magna  Daphnia pulex Family: Macrothricidae  Macrothrix rosea Family: Chydoridae  Chydorous sphaericus Family: Moinidae  Moina brachiata Family: Cyclopoida  Cyclops scutifera  Cyclops bicuspidatus Family: Cypridae  Cypris subglobosa Fig 3 : Dominance pattern of different Crustacean families in Anchar lake. Ahangar et al
  • 4. - 21 - CONCLUSION The maximum population of crustacea occurred in summer and spring time when temperature, dissolved oxygen were conducive and the food source in the form of phytoplankton and microbial organic matter was in abundance. Most of the crustacean species recorded from the lake was common in both the areas as they are free swimming forms and have better locomotory power than Rotifers. ACKNOWLEDGEMENTS The authors are highly thankful to the Senior Research Scholars of Aquatic Biology Laboratory, School of Studies in Zoology, Jiwaji University, Gwalior and Hydrobiology Research Laboratory, Govt. S. P. College, Srinagar for their valuable guidance and timely help. REFERENCES 1. Edmondson, W. T., (1959). Ward and Whipple’s Freshwater Biology, 2nd Ed. John Wiley and Sons, INC. New York. 2. A. P. H. A. (1998). Standard Methods for Examination of water and wastewater. 20th Ed. American Public Health Association, Washington, D.C. 3. Pennak, R.W. (1957). Species composition of limnetic zooplankton communities. Limnol.Oceanogr. 2(3): 222-223. 4. Battish, S. K. (1992). Freshwater zooplankton of India. Oxford and IBH publications, New Delhi. 5. Adoni, A. D. (1985). Workbook of Limnology. Pratibha Publications, Sagar. 6. Yousuf, A. R. (1989). Zooplankton studies in India with special references to North India. A critical review. Management of Aquatic Ecosystem. P. 309-324. 7. Schmitz, D. C. and Osborne, J. A. (1984). Zooplankton densities in a Hydrilla infested lake. Hydrobol. 111:127-132. 8. Beaver, J. R., Lemke, A. M. and Acton, J. K. (1999). Midsummer zooplankton assemblages in four types of wetlands in the upper Midwest, USA. Hydrobiol. 308: 209-220. 9. Smyly, W. J. P., (1958). Distribution and seasonal abundance of Entomostraca in Moorland ponds near Windermere. Hydrobiol. 11: 59-72. 10. Straskraba, M. (1965). Quantitative study of the littoral zooplankton of the rich vegetation of the backwater Labicko. Hydrobiol. 26:421-433. 11. Cowell, B. C., Dyne, C. W. and Adama, R. C. (1975). A synoptic study of the limnology of lake Thonotosassa, Florida. Effects of primary treated sewage and citrus wastes. 12. Nordlie, R. G. (1976). Plankton communities of three Central Florida lakes. Hydrobiol.48:65-78. 13. Pandit, A. K. (1980). Biotic Factor and Food Chain Structure in Some Typical Wetlands of Kashmir. Ph. D. Thesis, University of Kashmir, Srinagar-6, J&K. 14. Das, S. M. (1956). A Quantitative studies on fluctuations of plankton in two Kumaon lakes, Nainital and Bhimtal (India). Acta. Hydrobiol., 2(1): 9-17. 15. Balkhi, S. M. H. and Yousuf, A. R. (1992). Community structure of crustacean plankton in relation to trophic conditions. Int. J. Ecol. & Env. Sci. 18:155-168. Ahangar et al