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ISSN: 2349-8889
Volume-6, Issue-3 (May 2019)
https://doi.org/10.31033/ijrasb.6.3.2
International Journal for Research in
Applied Sciences and Biotechnology
www.ijrasb.com
Effect of Climate Change on Copepods Diversity in a Subtropical Pond
of Jammu
S. Kumar
Associate Professor, Department of Zoology, Bareilly College, Bareilly, INDIA
Corresponding Author: drsunilzoology@gmail.com
ABSTRACT
The prevalence of copepods that constitute an
important role in food chain of aquatic ecosystem and act as
indicators of productivity were examined in Kunjwani pond,
Jammu. Five copepod species, Cyclops vicinus, Mesocyclops
hyalinus, M. leukarti, Paracyclops fimbriatus and
Neodiaptomus diaphorus were recorded along with their
different level of developmental stages like nauplius,
metanauplius and copepodite. These exhibited trimodal
peaks during March, June and October. The data revealed
that their distribution is correlated with physico-chemical
factors. January to June higher density may be influenced
by temperature (19.89-34.5 0
C), suspended matter (50.0-
112.5 mg/l.), pH (7.58-9.98), DO (2.68-11.0 mg/l.), Ca++
(12.49-31.30 mg/l.) and Mg++ (2.64-8.68 mg/l.). The species
diversity index ranged between 0.9583-1.6539.
Keywords-- Copepods, Physico-Chemical Analysis,
Species Diversity Index
I. INTRODUCTION
Copepods comprise 70-80 % of the total
zooplankton population (Anonymous, 1991). They feed
on diatoms, bacteria and minute particles of organic
material in the water and in turn serve as food for many
of the larger aquatic animals, chiefly fish. Thus, they play
an important role in the food chain of aquatic ecosystem
at various trophic levels and act as indicators of
productivity. Based on these, various studies have been
carried out in India by Sewell (1940, 1957), Sehgal
(1983), Babar and Choubey (1987), Patil and Gounder
(1989), Kanagasabapathi and Rajan (2010), Saba and
Sadhu (2015), Shivkami et. al. (2015) and Sinha and
Singh (2016). The present study aims to examine the
community structure of copepods in relation to various
physico-chemical parameters.
II. MATERIALS AND METHODS
Water and plankton samples were collected
fortnightly from four sites during 1989-1990 and
analysed by adopting the methods of APHA (1985)
.Plankton samples were preserved in five percent
formalin and counted in Sedgwick rafter cell ( Welch,
1952). Identification were done as per description by
Ward and Whipple (1959) and Sehgal (1983). The
organisms expressed as nosl-1
and results are discussed as
the mean of four study sites. Statistical evaluation of data
were done as outlined by Trivedy et. al. (1987) and
Shannon and Weaver (1963).
III. RESULTS AND DISCUSSION
A number of inter-dependent abiotic and biotic
environmental factors influence the plankton dynamics in
different biotopes. Copepoda represented by five species
(Cyclops vicinus, Mesocyclops hyalinus, M. leukarti,
Paracyclops fimbriatus and Neodiaptomus diaphorus)
and their larvae (nauplius, metanauplius and copepodite).
Copepods have registered their seasonal association in
this pond. Monthly population density in percent
composition is given in Table 1.
Table 1- Percent composition of copepoda in kunjwani pond, Jammu
Apr May Jun Jul Aug Sep
Cyclops vicinus 6.25 4.9 - - - -
Mesocyclops hyalinus 15.62 21.72 15.07 10.71 53.44 12.5
M. leukarti - 2.45 - - - -
Paracyclops fimbriatus 22.91 24.59 6.58 4.91 15.51 12.5
Neodiaptomus diaphorus 5.2 9.01 - - 15.51 25
Nauplius 44.27 37.29 33.12 35.26 5.17 -
Metanauplis 2.08 - 43.73 48.21 5.17 25
Copepodite 3.64 - 1.48 0.89 5.17 25
4 This work is licensed under Creative Commons Attribution 4.0 International License.
ISSN: 2349-8889
Volume-6, Issue-3 (May 2019)
https://doi.org/10.31033/ijrasb.6.3.2
International Journal for Research in
Applied Sciences and Biotechnology
www.ijrasb.com
Oct Nov Dec Jan Feb Mar
Cyclops vicinus - - - 11.42 36.36 -
Mesocyclops hyalinus - - 3.65 9.71 12.12 12.48
M. leukarti - - - - - -
Paracyclops fimbriatus - - 3.65 22.28 4.76 7.64
Neodiaptomus diaphorus 100 58.82 47.56 35.42 14.71 66.98
Nauplius - - 37.8 3.42 26.83 6.87
Metanauplis - 23.52 7.31 16 2.59 5.42
Copepodite - 17.64 - 1.71 2.59 0.58
Table 2- Coefficient of correlation between Copepoda
and various abiotic factors
Factors Copepoda ® ( r )
Air temperature 0.111
Water temperature 0.134
Depth -0.168
Transparency 0.249**
Suspended matter -0.148
0.192*
Dissolved oxygen 0.029
Free carbondioxide -0.065
Carbonate 0.047
Bicarbonate 0.004
Chloride 0.196*
Calcium -0.094
Magnesium -0.061
Total Hardness -0.044
n = 48, **p<0.05, *p<0.1
Table 3- Coefficient of correlation between copepod and
other group of zooplankton
Groups Copepoda ( n - 48) ( r )
Protozoa -0.17
Rotifera -0.084
Cladocera -0.058
Ostracoda -0.067
Total Zooplankton 0.056
( n = 48 ) non significant
Table 4- Shannon Weaver species diversity index for
copepoda
Months Sp. Div. Index
Apr 1.5159
May 1.4995
Jun 1.2538
Jul 1.148
Aug 1.3719
Sep 1.559
Oct 1.2589
Nov 0.9583
Dec 1.1535
Jan 1.6539
Feb 1.5921
Mar 1.0959
The copepods dominated over other groups
during spring and summer season. Percentage
composition of this group indicated inverse relationship
between calanoids and cyclopoids. Sehgal (1983) stated
that ponds with high density of calanoids contained only
a few cyclopoids species and vice-versa. These two
planktonic forms are never found in equal proportions in
the same habitat . Larval stages of this group reported
highest density in June (369 nosl-1
) and march (133 nosl-
1
). Minimum density, noticed during August to November
with its absence in October.
January to June increase in copepods seem to be
influenced by temperature (19.89 – 34.50
c), suspended
matter (50.0 – 112.5 mg/l) pH (7.58 – 9.98), DO (2.68 –
11.0 mg/l), Ca++ (12.49 – 31.30 mg/l) and Mg++ (2.64 –
8.68 mg/l) and showed maximum density in March (1033
nosl-1
). Minimum density of this group was usually
observed during monsoon (August – September) and
winter (November – December) season.
The low population density in August –
September followed by the dilution effect and production
of resting stages by some copepods in response to
unfavourable conditions such as rise in water level,
increase in suspended matter, low light penetration and
food etc. Effect of winter rains and low temperature may
explain low production of copepods noticed during
November- December. Wierzbica (1966) documented
that a number of cyclopoids enter into various periods of
diapause either at egg stage or in copepodite stage with or
without encystment at sediments.
The coefficient of correlation between copepoda
with abiotic and biotic factors are presented in Table 2
5 This work is licensed under Creative Commons Attribution 4.0 International License.
ISSN: 2349-8889
Volume-6, Issue-3 (May 2019)
https://doi.org/10.31033/ijrasb.6.3.2
International Journal for Research in
Applied Sciences and Biotechnology
www.ijrasb.com
and 3. The numerical value of species diversity index of
copepoda ranged between 0.9589 – 1.6539 (Table
4).According to Sehgal (1983) that copepods are found in
turbid as well as clear water infested with aquatic weeds
(Hydrilla, Vallisnaria, Potamogeton and Najas) with
water temperature (25.70 – 31.50
c), pH ( 7.2 – 8.8), DO (
6.6- 7.8 ppm) and total alkalinity ( 160 – 220 ppm ). The
ranges are similar to the present findings. It is generally
thought that water temperature and transparency plays an
exceedingly important role in the activity and distribution
of copepods.
ACKNOWLEDGEMENT
The author is grateful to Head, Department of
Biosciences, University of Jammu, Jammu for providing
the laboratory facilities.
REFERENCES
[1] Anonymous (1991). Animal Resources of India. State
of Art. Zoological Survey of India, Calcutta : 73.
[2] APHA, (1985). Standard Methods for Examination of
Water and Wastewater. 16th edition, APHA Inc. New
York 1193.
[3] Babar, V. and Choubey, U. (1987). Studies on the
Copepod fauna of Gandhisagar Reservior. Pers. In
Hydrobiol. (eds. K. S. Rao and S. Shrivastava). Vikram
Univ. Ujjain. Sec. 4 (26) : 135-138.
[4] Kanagasabapathi, V. and Rajan, M.K. (2010). A
Preliminary Survey of Plankton In Irrukkangudi
Reservior, Virudhunagar dist., T.N. India. J. Phytology,
2(3): 63-72.
[5] Patil, C.S. and Gounder, B.Y.M. (1989). Freshwater
invertebrates of Dharwad, Prasaranga, Karnataka Univ.
Dharwad.
[6] Saba, F. and Sadhu, D.N. (2015). Zooplankton
diversity of Ganga Reservior of Bokaro, Jharkhand. Int.
J. Bioassays, 4(4) : 3792-3795.
[7] Sehgal, K.L. (1983). Planktonic Copepods of
Freshwater Ecosystem, Interprint, New Delhi, Sec. 4
(36): 1-169.
[8] Sewell, R.B.S. (1940). Fauna of Chilika lake
Crustacea; Copepda; Mem. Ind. Mus. 5 : 771-851.
[9] Sewell, R.B.S. (1957). A review of the subgenus
Thermocyclops Kiefer of genus Mesocyclops Sars with a
description of a new form of copepod, Rec. Ind. Mus. 55
(1) : 69-117.
[10] Shannon, G.E. and Weaver, W. (1963). The
mathematical theory of Communication. Univ. Illinois’s
Press, Urhana USA.
[11] Sinha, P.K. and Singh, R. (2016). Seasonal
zooplankton diversity in relation to physico-chemical
parameters of perennial pond of Chaibasa, West
Singhbhum, Jharkhand. Int. J. of Bioassays, 5(9): 4906-
4908.
[12] Sivakami, R., Arumugam, V. and Premkishor, G.
(2015). An analysis of zooplankton in a ake,Pudukkottai,
dist, Tamilnadu. Int. J. Curr. Microbiol. App. Sci. 4(5):
377-389.
[13] Trivedy, R.K., Goel, P.K. and Trisal, C.L. (1987).
Practical methods in Ecology and Environmential
Sciences, Environmental publications, Post box 60,
Karad, India.
[14] Ward, H.B. and Whipple, G.C.(1959). Freshwater
Biology. John Wiley and Sons, Inc. New York.
[15] Welch, P.S. (1952). Limnological methods, Mc-
Graw Hill book Co., Inc. New York.
[16]Wierzbicka, M. (1966). Les resultata des recherches
concernant letal de repos (restingStage) des cyclopoida.
Verh. Int. Ver. Limnol, 16 : 592-599.

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Effect of Climate Change on Copepods Diversity in a Subtropical Pond of Jammu

  • 1. 3 This work is licensed under Creative Commons Attribution 4.0 International License. ISSN: 2349-8889 Volume-6, Issue-3 (May 2019) https://doi.org/10.31033/ijrasb.6.3.2 International Journal for Research in Applied Sciences and Biotechnology www.ijrasb.com Effect of Climate Change on Copepods Diversity in a Subtropical Pond of Jammu S. Kumar Associate Professor, Department of Zoology, Bareilly College, Bareilly, INDIA Corresponding Author: drsunilzoology@gmail.com ABSTRACT The prevalence of copepods that constitute an important role in food chain of aquatic ecosystem and act as indicators of productivity were examined in Kunjwani pond, Jammu. Five copepod species, Cyclops vicinus, Mesocyclops hyalinus, M. leukarti, Paracyclops fimbriatus and Neodiaptomus diaphorus were recorded along with their different level of developmental stages like nauplius, metanauplius and copepodite. These exhibited trimodal peaks during March, June and October. The data revealed that their distribution is correlated with physico-chemical factors. January to June higher density may be influenced by temperature (19.89-34.5 0 C), suspended matter (50.0- 112.5 mg/l.), pH (7.58-9.98), DO (2.68-11.0 mg/l.), Ca++ (12.49-31.30 mg/l.) and Mg++ (2.64-8.68 mg/l.). The species diversity index ranged between 0.9583-1.6539. Keywords-- Copepods, Physico-Chemical Analysis, Species Diversity Index I. INTRODUCTION Copepods comprise 70-80 % of the total zooplankton population (Anonymous, 1991). They feed on diatoms, bacteria and minute particles of organic material in the water and in turn serve as food for many of the larger aquatic animals, chiefly fish. Thus, they play an important role in the food chain of aquatic ecosystem at various trophic levels and act as indicators of productivity. Based on these, various studies have been carried out in India by Sewell (1940, 1957), Sehgal (1983), Babar and Choubey (1987), Patil and Gounder (1989), Kanagasabapathi and Rajan (2010), Saba and Sadhu (2015), Shivkami et. al. (2015) and Sinha and Singh (2016). The present study aims to examine the community structure of copepods in relation to various physico-chemical parameters. II. MATERIALS AND METHODS Water and plankton samples were collected fortnightly from four sites during 1989-1990 and analysed by adopting the methods of APHA (1985) .Plankton samples were preserved in five percent formalin and counted in Sedgwick rafter cell ( Welch, 1952). Identification were done as per description by Ward and Whipple (1959) and Sehgal (1983). The organisms expressed as nosl-1 and results are discussed as the mean of four study sites. Statistical evaluation of data were done as outlined by Trivedy et. al. (1987) and Shannon and Weaver (1963). III. RESULTS AND DISCUSSION A number of inter-dependent abiotic and biotic environmental factors influence the plankton dynamics in different biotopes. Copepoda represented by five species (Cyclops vicinus, Mesocyclops hyalinus, M. leukarti, Paracyclops fimbriatus and Neodiaptomus diaphorus) and their larvae (nauplius, metanauplius and copepodite). Copepods have registered their seasonal association in this pond. Monthly population density in percent composition is given in Table 1. Table 1- Percent composition of copepoda in kunjwani pond, Jammu Apr May Jun Jul Aug Sep Cyclops vicinus 6.25 4.9 - - - - Mesocyclops hyalinus 15.62 21.72 15.07 10.71 53.44 12.5 M. leukarti - 2.45 - - - - Paracyclops fimbriatus 22.91 24.59 6.58 4.91 15.51 12.5 Neodiaptomus diaphorus 5.2 9.01 - - 15.51 25 Nauplius 44.27 37.29 33.12 35.26 5.17 - Metanauplis 2.08 - 43.73 48.21 5.17 25 Copepodite 3.64 - 1.48 0.89 5.17 25
  • 2. 4 This work is licensed under Creative Commons Attribution 4.0 International License. ISSN: 2349-8889 Volume-6, Issue-3 (May 2019) https://doi.org/10.31033/ijrasb.6.3.2 International Journal for Research in Applied Sciences and Biotechnology www.ijrasb.com Oct Nov Dec Jan Feb Mar Cyclops vicinus - - - 11.42 36.36 - Mesocyclops hyalinus - - 3.65 9.71 12.12 12.48 M. leukarti - - - - - - Paracyclops fimbriatus - - 3.65 22.28 4.76 7.64 Neodiaptomus diaphorus 100 58.82 47.56 35.42 14.71 66.98 Nauplius - - 37.8 3.42 26.83 6.87 Metanauplis - 23.52 7.31 16 2.59 5.42 Copepodite - 17.64 - 1.71 2.59 0.58 Table 2- Coefficient of correlation between Copepoda and various abiotic factors Factors Copepoda ® ( r ) Air temperature 0.111 Water temperature 0.134 Depth -0.168 Transparency 0.249** Suspended matter -0.148 0.192* Dissolved oxygen 0.029 Free carbondioxide -0.065 Carbonate 0.047 Bicarbonate 0.004 Chloride 0.196* Calcium -0.094 Magnesium -0.061 Total Hardness -0.044 n = 48, **p<0.05, *p<0.1 Table 3- Coefficient of correlation between copepod and other group of zooplankton Groups Copepoda ( n - 48) ( r ) Protozoa -0.17 Rotifera -0.084 Cladocera -0.058 Ostracoda -0.067 Total Zooplankton 0.056 ( n = 48 ) non significant Table 4- Shannon Weaver species diversity index for copepoda Months Sp. Div. Index Apr 1.5159 May 1.4995 Jun 1.2538 Jul 1.148 Aug 1.3719 Sep 1.559 Oct 1.2589 Nov 0.9583 Dec 1.1535 Jan 1.6539 Feb 1.5921 Mar 1.0959 The copepods dominated over other groups during spring and summer season. Percentage composition of this group indicated inverse relationship between calanoids and cyclopoids. Sehgal (1983) stated that ponds with high density of calanoids contained only a few cyclopoids species and vice-versa. These two planktonic forms are never found in equal proportions in the same habitat . Larval stages of this group reported highest density in June (369 nosl-1 ) and march (133 nosl- 1 ). Minimum density, noticed during August to November with its absence in October. January to June increase in copepods seem to be influenced by temperature (19.89 – 34.50 c), suspended matter (50.0 – 112.5 mg/l) pH (7.58 – 9.98), DO (2.68 – 11.0 mg/l), Ca++ (12.49 – 31.30 mg/l) and Mg++ (2.64 – 8.68 mg/l) and showed maximum density in March (1033 nosl-1 ). Minimum density of this group was usually observed during monsoon (August – September) and winter (November – December) season. The low population density in August – September followed by the dilution effect and production of resting stages by some copepods in response to unfavourable conditions such as rise in water level, increase in suspended matter, low light penetration and food etc. Effect of winter rains and low temperature may explain low production of copepods noticed during November- December. Wierzbica (1966) documented that a number of cyclopoids enter into various periods of diapause either at egg stage or in copepodite stage with or without encystment at sediments. The coefficient of correlation between copepoda with abiotic and biotic factors are presented in Table 2
  • 3. 5 This work is licensed under Creative Commons Attribution 4.0 International License. ISSN: 2349-8889 Volume-6, Issue-3 (May 2019) https://doi.org/10.31033/ijrasb.6.3.2 International Journal for Research in Applied Sciences and Biotechnology www.ijrasb.com and 3. The numerical value of species diversity index of copepoda ranged between 0.9589 – 1.6539 (Table 4).According to Sehgal (1983) that copepods are found in turbid as well as clear water infested with aquatic weeds (Hydrilla, Vallisnaria, Potamogeton and Najas) with water temperature (25.70 – 31.50 c), pH ( 7.2 – 8.8), DO ( 6.6- 7.8 ppm) and total alkalinity ( 160 – 220 ppm ). The ranges are similar to the present findings. It is generally thought that water temperature and transparency plays an exceedingly important role in the activity and distribution of copepods. ACKNOWLEDGEMENT The author is grateful to Head, Department of Biosciences, University of Jammu, Jammu for providing the laboratory facilities. REFERENCES [1] Anonymous (1991). Animal Resources of India. State of Art. Zoological Survey of India, Calcutta : 73. [2] APHA, (1985). Standard Methods for Examination of Water and Wastewater. 16th edition, APHA Inc. New York 1193. [3] Babar, V. and Choubey, U. (1987). Studies on the Copepod fauna of Gandhisagar Reservior. Pers. In Hydrobiol. (eds. K. S. Rao and S. Shrivastava). Vikram Univ. Ujjain. Sec. 4 (26) : 135-138. [4] Kanagasabapathi, V. and Rajan, M.K. (2010). A Preliminary Survey of Plankton In Irrukkangudi Reservior, Virudhunagar dist., T.N. India. J. Phytology, 2(3): 63-72. [5] Patil, C.S. and Gounder, B.Y.M. (1989). Freshwater invertebrates of Dharwad, Prasaranga, Karnataka Univ. Dharwad. [6] Saba, F. and Sadhu, D.N. (2015). Zooplankton diversity of Ganga Reservior of Bokaro, Jharkhand. Int. J. Bioassays, 4(4) : 3792-3795. [7] Sehgal, K.L. (1983). Planktonic Copepods of Freshwater Ecosystem, Interprint, New Delhi, Sec. 4 (36): 1-169. [8] Sewell, R.B.S. (1940). Fauna of Chilika lake Crustacea; Copepda; Mem. Ind. Mus. 5 : 771-851. [9] Sewell, R.B.S. (1957). A review of the subgenus Thermocyclops Kiefer of genus Mesocyclops Sars with a description of a new form of copepod, Rec. Ind. Mus. 55 (1) : 69-117. [10] Shannon, G.E. and Weaver, W. (1963). The mathematical theory of Communication. Univ. Illinois’s Press, Urhana USA. [11] Sinha, P.K. and Singh, R. (2016). Seasonal zooplankton diversity in relation to physico-chemical parameters of perennial pond of Chaibasa, West Singhbhum, Jharkhand. Int. J. of Bioassays, 5(9): 4906- 4908. [12] Sivakami, R., Arumugam, V. and Premkishor, G. (2015). An analysis of zooplankton in a ake,Pudukkottai, dist, Tamilnadu. Int. J. Curr. Microbiol. App. Sci. 4(5): 377-389. [13] Trivedy, R.K., Goel, P.K. and Trisal, C.L. (1987). Practical methods in Ecology and Environmential Sciences, Environmental publications, Post box 60, Karad, India. [14] Ward, H.B. and Whipple, G.C.(1959). Freshwater Biology. John Wiley and Sons, Inc. New York. [15] Welch, P.S. (1952). Limnological methods, Mc- Graw Hill book Co., Inc. New York. [16]Wierzbicka, M. (1966). Les resultata des recherches concernant letal de repos (restingStage) des cyclopoida. Verh. Int. Ver. Limnol, 16 : 592-599.