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Article Citation:
Patil MU, Patole SS, Bhoi SS and Ahirrao KD
Malacofaunal distribution, abundance and diversity of the Nakana Lake, Dhule (MS)
India.
Journal of Research in Biology (2016) 6(2): 1977-1983
JournalofResearchinBiology
Malacofaunal distribution, abundance and diversity of the Nakana Lake,
Dhule (MS) India
ABSTRACT:
Freshwater Molluscs distribution and diversity status of Nakana Lake, Dhule,
were studied during June 2013 to May 2014. The samples were collected at every
fortnight from two sites. A total of 13 species were reported, out of which 10 species
were Gastropods and three species were Pelecypods; those belonged to four orders,
10 families and 12 genera. The abundance of molluscs was also studied. The average
number of animals were indicated per season: i.e. monsoon, winter and summer.
Maximum species were collected in the summer season at both the sites. Molluscan
diversity were calculated by the various diversity indices such as Shannon-Wiener
diversity index (H), Simpson’s Dominance index (D), Simpson’s index of diversity (I-D),
Simpson’s Evenness(E) and Pielou’s Evenness index (J).
1977-1983 | JRB | 2016 | Vol 6 | No 2
This article is governed by the Creative Commons Attribution License (http://creativecommons.org/
licenses/by/4.0), which gives permission for unrestricted use, non-commercial, distribution and
reproduction in all medium, provided the original work is properly cited.
www.jresearchbiology.com
Journal of Research in Biology
An International
Scientific Research Journal
Authors:
Patil MU1
Patole SS2
,
Bhoi SS3
and
Ahirrao KD4
Institution:
1. Dept. of Zoology, V.U.
Patil Arts, and Late Dr. B. S.
Desale science college,
Sakri, Dist-Dhule 424304.
2. Dept. of Zoology,
V,V,M.’s S.G. Patil Arts
Science and Commerce
College, Sakri, District-
Dhule.
3. Dept. of Zoology,
Uttamrao. Patil Arts, and
science college, Dahivel,
Tal. Sakri, Dist-Dhule.
4. Head, Dept of Zoology,
Rani Laxmibai College,
Parola, Dist-Jalgaon 425
111.
Corresponding author:
Patil Manisha U
Email Id:
Web Address:
http://jresearchbiology.com/
documents/RA0584.pdf
Dates:
Received: 09 Dec 2016 Accepted: 18 Jan 2016 Published: 04 March 2016
Journal of Research in Biology
An International Scientific Research Journal
Original Research
ISSN No: Print: 2231 –6280; Online: 2231- 6299
Keywords:
Molluscan diversity, Seasonal variations, Abundance, Biological Indices.
INTRODUCTION
The mollusca are soft bodied animals. They
move on the land and still dependent on a moist ground,
in an excess of cold or hot and dry climate they enter in
the state of dormancy. The Phylum Mollusca are
classified into seven classes viz. Aplacophora,
Polyplacophora, Monoplacophora, Gastropoda,
Scaphopoda, Pelecypoda, and Cephalopoda. Gastropoda
is the largest class more than 80,000 species are recorded
throughout the world. (Hyman, 1967).
Mollusca prove immensely beneficial in
economic and medicinal values. Like all animals, the
molluscs are not considered by men to be either useful or
destructive. Gastropod plays an important role in
balanceing the nature. The shells were used in Unani and
Ayurvedic medicine system for meditation, in the
production of humus, in the control of fungi, algae,
lichens and also as predators and parasites; but in nature
the molluscs are hunted and eaten by predators (Ahirrao,
2003).
In scientific studies, molluscs prove key role in
study of drug action on heart, hormones, enzymes and
antitoxins-especially in relation to immunological
haematology. These are suitable bioindicators for some
radio-active and chemical pollution in the coastal areas
of water bodies. The snails and slugs are important to
man because of the damage they do in agriculture,
horticulture and forestry. Furthermore, they are of
importance in medical and veterinary practice, since they
serve as intermediate host for certain parasitic worms of
man and domestic animals viz. Schistosome parasites
(Ahirrao, 2003; Ahirrao and Khedkar, 2012).
MATERIALS AND METHODS
Geographical area of Nakana Lake
The present study area is selected from one of the
man-made Lake situated on the Panzara River, 6 km
away from Dhule city. It runs parallel to the National
highway number: 6 (NH-6). Geographical location of the
lake is as follows; Longitudes:- 74.7417477 and
Latitudes:- 20.9095349. It is an earthen lake having
catchment area of 945 m3
, with a maximum height is
18.41 m. It also receives water from Haranmall Lake.
The lake water is used for drinking, irrigation and
aquaculture purpose. One side of it is covered by a well
developed forest with grass trees, herbs and shrubs. The
grass starts in the forest drying from the start of post
monsoon, frequently cattle grazing is observed in this
Patil et al., 2016
1978 Journal of Research in Biology (2016) 6(2):1977-1983
Figure 1. Map Showing Study area, Nakana Lake, Dhule (MS) India
area. During present investigation two sites were selected
for the study namely S-I and S-II.
Sampling and preservation
The Molluscan species were collected by hand
picking method for the big specimens and for the
smallest one, a sieve for soil samples were used. All
specimens were brought to the laboratory, washed
thoroughly, and preserved in 4 % formalin. The shells
were dried at room temperature, and then separated in
polythene bags. Identification was done on the basis of
Preston (1915) Rao (1989) and Tonapi (1980). The
unidentified molluscan shells are identified and classified
upto the generic and species level by Zoological survey
of India, Pune, Maharashtra State, India. Data were
collected fortnightly, pooled seasonally viz. monsoon,
winter and summer from June 2013 to May 2014.
Data analysis
Quantitative and qualitative estimation of
molluscan fauna were carried out using quadrat method
(Micheal, 1984, Subba Rao, 1989). At least four quadrat
(1 X 1m) were sampled from each site and the average of
these were considerd as density and species richness per
m2
for that area.
Formulae for indices
Total number of species, total number of
individual in a sample and different diversity indices.
From the present data were calculated using the
following indices Shannon-Weiner Index (H) (1949),
Simpson’s Dominance Index (D), Simpson (1949),
Simpson’s Index of diversity (1-D), Simpson’s reciprocal
Journal of Research in Biology (2016) 6(2):1977-1983 1979
Patil et al., 2016
S. No. Index
Site -I Site-II
M W S M W S
1 Species Richness (S) 13 13 13 12 12 12
2 Species abundance(N) 54 80 137 37 50 104
3 Shannon-Weiner Index(H)
3.8134 3.0866 6.5137 3.058 2.2611 5.2641
4 Simpson’s Dominance Index (D) 0.0887 0.1183 0.1212 0.1216 0.1461 0.1376
5 Simpson’s Index of Diversity (1-D) 0.9113 0.8817 0.8788 0.8784 0.8539 0.8624
6 Simpson’s reciprocal Index (1/D) 11.273 8.453 8.2508 8.2226 6.8446 7.2674
7 Simpson’s Evenness (E) 0.8671 0.6502 0.6346 0.6853 0.5703 0.6056
8 Pielou’s Evenness (J) 1.4867 1.2033 2.5395 1.2306 0.9099 2.1184
Table 1. The Molluscan species richness, abundance and diversity indices of Nakana Lake and Dhule are
tabulated.
Figure 2. Photographs showing the study areas (i) S-I and (ii) S-II.
(i) (ii)
Index (1/D), Simpson’s Evenness (E) and Pielou’s
evenness Index (J) Pielou(1975). The following index
values were used for calculation.
RESULTS AND DISCUSSION
Seasonal variations
In the present investigation 462, samples were
collected during June 2013 to May 2014 from the both
sites i.e. Site I (Nakana Lake) and site II (Dhule).
Totally, 13 species were recorded, which belongs to 4
orders, 10 families and 12 genera. Among them
Gastropods found to be dominant over Pelecypods, it
contributes 86.14% and 13.65 % respectively. Sharma
et.al. (2009), recorded similar predominance of
Gastropoda over Pelecepoda. From Site I =13 species,
and from Site II =12 species were recorded. This is
shown in Fig.3.
Density of Mollusca at Site-I ranges between 54
organism/m2
in monsoon , 80 org./m2
in winter and 137
org./m2
in summer season, whereas at Site-II, least 37
org./m2
in Monsoon, moderate number 50 org./m2
in
Winter and maximum i.e. 104 org./m2
in Summer.
Observations showed that highest population of
Molluscs were recorded during summer from both the
sites that are corresponding with Hussein et al.,(2011).
He reported March-May pick in his study. The snail
abundance was maximum during the summer which
might be due to ecological conditions like warm
temperature, activates the process of decomposition. A
large amount of decomposers is responsible for the
deposition of organic matter and macrophytes at the
bottom of the lake.
Total decline in molluscan population was
Patil et al., 2016
1980 Journal of Research in Biology (2016) 6(2):1977-1983
Figure 3. Pie Charts showing percentage of annual distribution of species at two sites: S-I and S-II respectively
1.Shannon – Weiner Index (H): H= -∑Pi (Ln Pi),
2.Simpson’s Dominance Index (D): D = ∑ n(n-1)/N(N-1),
3.Simpson’s Index of Diversity (D1): D1 = 1-D,
4.Simpson’s reciprocal Index (D2 ): D2 = 1/D,
5.Simpson’s Evenness (E): E = D2/S
6.Pielou’s evenness Index (J): J = H/Ln*S
Where,
S = Number of species.
N = Total number of individual of all species.
Pi = A/T where A is number of each species in the sample,
T = Total number of individual of all species in the sample.
n = Total number of individuals of particular species.
observed at monsoon season due to self dilution of the
body fluid. The sensitive molluscs could not adjust the
fluctuating osmotic balance suddenly hence the mortality
was very high during the period of monsoon season. The
salinity and temperature dropped down which is made
the condition adverse for the animal because of heavy
rainfall, Patole (2010).
In winter at both sites population of molluscs
found to be moderate in number, because of the suitable
ecosystem but molluscans are poikilotherms, and they
cannot tollerate tolerate an excess cold environment and
hence they may enter in to the state of hibernation. On
the other hand El-Kady et al., (2000) was recorded low
number of snails during winter (Jan and Feb) in Sinai
Peninsula.
Biological indices
The diversity of molluscs mainly depends up on
biotic, abiotic factors and stability of the ecosystem.
Molluscan diversity is calculated by the diversity status,
richness, abundance, habitat and various diversity
indices. Values are shown in table no. 1.
For proper understanding the Biotic community,
it is essential to work out some indices Sharma et al.,
(2010). There has been quite large fluctuation between
the level of abundance and showed great diversity of
molluscs during the one year study period. The Nakana
Lake shows Shannon-Weiner Index (H) varied from
6.5137 to 3.0866 at Site-I and at Site –II in between
5.2641 to 2.2611. Simpson’s Dominance Index (D)
fluctuated in between 0.0887 and 0.1216 in Monsoon,
0.1183 and 0.1461 in Winter and 0.1212 and 0.1376 in
Summer, where, Sit-II was found to be dominant over
Site-I. Values of Simpson’s Index of Diversity at site –I
is found to be varied i.e. 0.9113 in Monsoon, 0.8817 in
Winter and 0.8788 in Summer Whereas, 0.8784 in
Monsoon, 0.8539 in Winter and 0.8624 in Summer, at
Site II. Simpson’s reciprocal Index (1/D) was highest in
Monsoon 11.273 and 8.2508 at Site-I and at Site-II and
least in Winter 8.453 and and 6.8446 respectively.
Simpson’s Evenness (E) maximum in Monsoon 0.8671
followed by Winter 0.6502 and Summer 0.6346 at Site-I
and at site II maximum recorded in Monsoon 0.6853
followed by 0.6056 in Summer, 0.5703 in Winter.
Pielou’s Evenness (J) ranges in between 2.5395 to
2.1184 in Summer season at Site-I and Site-II
respectively while 0.9099 to 1.2033 in Winter and
Journal of Research in Biology (2016) 6(2):1977-1983 1981
Patil et al., 2016
Figure 4. The column chart shows comparison amoung different diversity indices of recorded molluscan
species, at Nakana Lake, Dhule.
1982 Journal of Research in Biology (2016) 6(2):1977-1983
Patil et al., 2016
1.4867 to 1.2306 in mosoon. The present investigation
resemble with the observation made by so many workers
on the occurrence of molluscan diversity in different
water bodies (Dolikar et al., 2014, Mohan et al., 2013).
CONCLUSION
In general, the present study revealed that species
richness, abundance, density and diversity of molluscans
depend upon rich ecosystem of Nakana Lake. All
recorded molluscan species are indigenous. There found
a considerable difference within the study localities.
ACKNOWLEDGEMENT
The authors are grateful to the Principal, S.G.
Patil, A.C. S. College, Sakri, Dist. Dhule (M.S), India,
for providing laboratory facilities during tenure of
research work and also thankful to ZSI, Pune for
scientific identification of Molluscan species.
REFERENCES
Ahirrao KD. (2003). Effect of sevin on some
ecophysiological aspects of a Melanoid snail, Melania
scabra. Ph. D. Thesis submitted to Dr. BAMU,
Aurangabad.
Ahirrao KD and Khedkar GD. (2012). Variations in
LC50 of some pesticides due to physic-chemical
parameters and impact of sevin on neurosecretory cells
of a fresh water snail, Thiara lineata, Journal of
Research in Biology, 1:050-056.
El-kady GA, Shoukry A, Reda LA, El-Badri YS.
(2000). Survey and population dynamics of fresh water
snail in newly settled areas of the Sinai Peninsula.
Egyptian Journal of Biology, 2:42-48.
Hussein MA, Obuid-Allah AH, Mahmoud AA,
Fangary HM. (2011). Population dynamics of fresh
water snails (Mollusca:Gastrapoda) at Qena
Governorate, Upper Egypt. Egypt. Acad. J. Biol. Sci., 3
(1):11-22.
Hyman LH. (1967). The invertebrates Vol.6. Mollusca,
1, McGraw Hill, New York.
Micheal P. (1984). Tata McGraw – Hill Publishing
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Patole VM. (2010). Ecology and biodiversity of
Mangroves in Mochemad estuary of Vengurla, South
Konkan, Maharashtra. Ph. D. Thesis submitted to
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Pielou EC. (1975). Ecological diversity. Wiley, New
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Sharma KK. Sharma SP and Sawhney N. (2009).
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Sharma KK, Samita Chowdhary and Arti Sharma.
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Subba Rao NV. (1989). Handbook: Freshwater molluscs
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Dolikar AV, Mohite AS and Charde PN. (2014).
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Mohan D, Elumalai V, Subbulakshmi G, Jaylakshami
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molluscan resources from Pulicat Lake, Southeast coast
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Shannon EC and Wiener W. (1949). The Mathematical
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Simpson EH. (1949). Measurement of diversity, Nature,
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Preston HB. (1915). The fauna of British India
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Rao SNV. (1989): Freshwater Mollusca of India. In. Rao
KS. (ED.). Recent advances in freshwater Biology. New
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Malacofaunal distribution, abundance and diversity of the Nakana Lake, Dhule (MS) India

  • 1. Article Citation: Patil MU, Patole SS, Bhoi SS and Ahirrao KD Malacofaunal distribution, abundance and diversity of the Nakana Lake, Dhule (MS) India. Journal of Research in Biology (2016) 6(2): 1977-1983 JournalofResearchinBiology Malacofaunal distribution, abundance and diversity of the Nakana Lake, Dhule (MS) India ABSTRACT: Freshwater Molluscs distribution and diversity status of Nakana Lake, Dhule, were studied during June 2013 to May 2014. The samples were collected at every fortnight from two sites. A total of 13 species were reported, out of which 10 species were Gastropods and three species were Pelecypods; those belonged to four orders, 10 families and 12 genera. The abundance of molluscs was also studied. The average number of animals were indicated per season: i.e. monsoon, winter and summer. Maximum species were collected in the summer season at both the sites. Molluscan diversity were calculated by the various diversity indices such as Shannon-Wiener diversity index (H), Simpson’s Dominance index (D), Simpson’s index of diversity (I-D), Simpson’s Evenness(E) and Pielou’s Evenness index (J). 1977-1983 | JRB | 2016 | Vol 6 | No 2 This article is governed by the Creative Commons Attribution License (http://creativecommons.org/ licenses/by/4.0), which gives permission for unrestricted use, non-commercial, distribution and reproduction in all medium, provided the original work is properly cited. www.jresearchbiology.com Journal of Research in Biology An International Scientific Research Journal Authors: Patil MU1 Patole SS2 , Bhoi SS3 and Ahirrao KD4 Institution: 1. Dept. of Zoology, V.U. Patil Arts, and Late Dr. B. S. Desale science college, Sakri, Dist-Dhule 424304. 2. Dept. of Zoology, V,V,M.’s S.G. Patil Arts Science and Commerce College, Sakri, District- Dhule. 3. Dept. of Zoology, Uttamrao. Patil Arts, and science college, Dahivel, Tal. Sakri, Dist-Dhule. 4. Head, Dept of Zoology, Rani Laxmibai College, Parola, Dist-Jalgaon 425 111. Corresponding author: Patil Manisha U Email Id: Web Address: http://jresearchbiology.com/ documents/RA0584.pdf Dates: Received: 09 Dec 2016 Accepted: 18 Jan 2016 Published: 04 March 2016 Journal of Research in Biology An International Scientific Research Journal Original Research ISSN No: Print: 2231 –6280; Online: 2231- 6299 Keywords: Molluscan diversity, Seasonal variations, Abundance, Biological Indices.
  • 2. INTRODUCTION The mollusca are soft bodied animals. They move on the land and still dependent on a moist ground, in an excess of cold or hot and dry climate they enter in the state of dormancy. The Phylum Mollusca are classified into seven classes viz. Aplacophora, Polyplacophora, Monoplacophora, Gastropoda, Scaphopoda, Pelecypoda, and Cephalopoda. Gastropoda is the largest class more than 80,000 species are recorded throughout the world. (Hyman, 1967). Mollusca prove immensely beneficial in economic and medicinal values. Like all animals, the molluscs are not considered by men to be either useful or destructive. Gastropod plays an important role in balanceing the nature. The shells were used in Unani and Ayurvedic medicine system for meditation, in the production of humus, in the control of fungi, algae, lichens and also as predators and parasites; but in nature the molluscs are hunted and eaten by predators (Ahirrao, 2003). In scientific studies, molluscs prove key role in study of drug action on heart, hormones, enzymes and antitoxins-especially in relation to immunological haematology. These are suitable bioindicators for some radio-active and chemical pollution in the coastal areas of water bodies. The snails and slugs are important to man because of the damage they do in agriculture, horticulture and forestry. Furthermore, they are of importance in medical and veterinary practice, since they serve as intermediate host for certain parasitic worms of man and domestic animals viz. Schistosome parasites (Ahirrao, 2003; Ahirrao and Khedkar, 2012). MATERIALS AND METHODS Geographical area of Nakana Lake The present study area is selected from one of the man-made Lake situated on the Panzara River, 6 km away from Dhule city. It runs parallel to the National highway number: 6 (NH-6). Geographical location of the lake is as follows; Longitudes:- 74.7417477 and Latitudes:- 20.9095349. It is an earthen lake having catchment area of 945 m3 , with a maximum height is 18.41 m. It also receives water from Haranmall Lake. The lake water is used for drinking, irrigation and aquaculture purpose. One side of it is covered by a well developed forest with grass trees, herbs and shrubs. The grass starts in the forest drying from the start of post monsoon, frequently cattle grazing is observed in this Patil et al., 2016 1978 Journal of Research in Biology (2016) 6(2):1977-1983 Figure 1. Map Showing Study area, Nakana Lake, Dhule (MS) India
  • 3. area. During present investigation two sites were selected for the study namely S-I and S-II. Sampling and preservation The Molluscan species were collected by hand picking method for the big specimens and for the smallest one, a sieve for soil samples were used. All specimens were brought to the laboratory, washed thoroughly, and preserved in 4 % formalin. The shells were dried at room temperature, and then separated in polythene bags. Identification was done on the basis of Preston (1915) Rao (1989) and Tonapi (1980). The unidentified molluscan shells are identified and classified upto the generic and species level by Zoological survey of India, Pune, Maharashtra State, India. Data were collected fortnightly, pooled seasonally viz. monsoon, winter and summer from June 2013 to May 2014. Data analysis Quantitative and qualitative estimation of molluscan fauna were carried out using quadrat method (Micheal, 1984, Subba Rao, 1989). At least four quadrat (1 X 1m) were sampled from each site and the average of these were considerd as density and species richness per m2 for that area. Formulae for indices Total number of species, total number of individual in a sample and different diversity indices. From the present data were calculated using the following indices Shannon-Weiner Index (H) (1949), Simpson’s Dominance Index (D), Simpson (1949), Simpson’s Index of diversity (1-D), Simpson’s reciprocal Journal of Research in Biology (2016) 6(2):1977-1983 1979 Patil et al., 2016 S. No. Index Site -I Site-II M W S M W S 1 Species Richness (S) 13 13 13 12 12 12 2 Species abundance(N) 54 80 137 37 50 104 3 Shannon-Weiner Index(H) 3.8134 3.0866 6.5137 3.058 2.2611 5.2641 4 Simpson’s Dominance Index (D) 0.0887 0.1183 0.1212 0.1216 0.1461 0.1376 5 Simpson’s Index of Diversity (1-D) 0.9113 0.8817 0.8788 0.8784 0.8539 0.8624 6 Simpson’s reciprocal Index (1/D) 11.273 8.453 8.2508 8.2226 6.8446 7.2674 7 Simpson’s Evenness (E) 0.8671 0.6502 0.6346 0.6853 0.5703 0.6056 8 Pielou’s Evenness (J) 1.4867 1.2033 2.5395 1.2306 0.9099 2.1184 Table 1. The Molluscan species richness, abundance and diversity indices of Nakana Lake and Dhule are tabulated. Figure 2. Photographs showing the study areas (i) S-I and (ii) S-II. (i) (ii)
  • 4. Index (1/D), Simpson’s Evenness (E) and Pielou’s evenness Index (J) Pielou(1975). The following index values were used for calculation. RESULTS AND DISCUSSION Seasonal variations In the present investigation 462, samples were collected during June 2013 to May 2014 from the both sites i.e. Site I (Nakana Lake) and site II (Dhule). Totally, 13 species were recorded, which belongs to 4 orders, 10 families and 12 genera. Among them Gastropods found to be dominant over Pelecypods, it contributes 86.14% and 13.65 % respectively. Sharma et.al. (2009), recorded similar predominance of Gastropoda over Pelecepoda. From Site I =13 species, and from Site II =12 species were recorded. This is shown in Fig.3. Density of Mollusca at Site-I ranges between 54 organism/m2 in monsoon , 80 org./m2 in winter and 137 org./m2 in summer season, whereas at Site-II, least 37 org./m2 in Monsoon, moderate number 50 org./m2 in Winter and maximum i.e. 104 org./m2 in Summer. Observations showed that highest population of Molluscs were recorded during summer from both the sites that are corresponding with Hussein et al.,(2011). He reported March-May pick in his study. The snail abundance was maximum during the summer which might be due to ecological conditions like warm temperature, activates the process of decomposition. A large amount of decomposers is responsible for the deposition of organic matter and macrophytes at the bottom of the lake. Total decline in molluscan population was Patil et al., 2016 1980 Journal of Research in Biology (2016) 6(2):1977-1983 Figure 3. Pie Charts showing percentage of annual distribution of species at two sites: S-I and S-II respectively 1.Shannon – Weiner Index (H): H= -∑Pi (Ln Pi), 2.Simpson’s Dominance Index (D): D = ∑ n(n-1)/N(N-1), 3.Simpson’s Index of Diversity (D1): D1 = 1-D, 4.Simpson’s reciprocal Index (D2 ): D2 = 1/D, 5.Simpson’s Evenness (E): E = D2/S 6.Pielou’s evenness Index (J): J = H/Ln*S Where, S = Number of species. N = Total number of individual of all species. Pi = A/T where A is number of each species in the sample, T = Total number of individual of all species in the sample. n = Total number of individuals of particular species.
  • 5. observed at monsoon season due to self dilution of the body fluid. The sensitive molluscs could not adjust the fluctuating osmotic balance suddenly hence the mortality was very high during the period of monsoon season. The salinity and temperature dropped down which is made the condition adverse for the animal because of heavy rainfall, Patole (2010). In winter at both sites population of molluscs found to be moderate in number, because of the suitable ecosystem but molluscans are poikilotherms, and they cannot tollerate tolerate an excess cold environment and hence they may enter in to the state of hibernation. On the other hand El-Kady et al., (2000) was recorded low number of snails during winter (Jan and Feb) in Sinai Peninsula. Biological indices The diversity of molluscs mainly depends up on biotic, abiotic factors and stability of the ecosystem. Molluscan diversity is calculated by the diversity status, richness, abundance, habitat and various diversity indices. Values are shown in table no. 1. For proper understanding the Biotic community, it is essential to work out some indices Sharma et al., (2010). There has been quite large fluctuation between the level of abundance and showed great diversity of molluscs during the one year study period. The Nakana Lake shows Shannon-Weiner Index (H) varied from 6.5137 to 3.0866 at Site-I and at Site –II in between 5.2641 to 2.2611. Simpson’s Dominance Index (D) fluctuated in between 0.0887 and 0.1216 in Monsoon, 0.1183 and 0.1461 in Winter and 0.1212 and 0.1376 in Summer, where, Sit-II was found to be dominant over Site-I. Values of Simpson’s Index of Diversity at site –I is found to be varied i.e. 0.9113 in Monsoon, 0.8817 in Winter and 0.8788 in Summer Whereas, 0.8784 in Monsoon, 0.8539 in Winter and 0.8624 in Summer, at Site II. Simpson’s reciprocal Index (1/D) was highest in Monsoon 11.273 and 8.2508 at Site-I and at Site-II and least in Winter 8.453 and and 6.8446 respectively. Simpson’s Evenness (E) maximum in Monsoon 0.8671 followed by Winter 0.6502 and Summer 0.6346 at Site-I and at site II maximum recorded in Monsoon 0.6853 followed by 0.6056 in Summer, 0.5703 in Winter. Pielou’s Evenness (J) ranges in between 2.5395 to 2.1184 in Summer season at Site-I and Site-II respectively while 0.9099 to 1.2033 in Winter and Journal of Research in Biology (2016) 6(2):1977-1983 1981 Patil et al., 2016 Figure 4. The column chart shows comparison amoung different diversity indices of recorded molluscan species, at Nakana Lake, Dhule.
  • 6. 1982 Journal of Research in Biology (2016) 6(2):1977-1983 Patil et al., 2016 1.4867 to 1.2306 in mosoon. The present investigation resemble with the observation made by so many workers on the occurrence of molluscan diversity in different water bodies (Dolikar et al., 2014, Mohan et al., 2013). CONCLUSION In general, the present study revealed that species richness, abundance, density and diversity of molluscans depend upon rich ecosystem of Nakana Lake. All recorded molluscan species are indigenous. There found a considerable difference within the study localities. ACKNOWLEDGEMENT The authors are grateful to the Principal, S.G. Patil, A.C. S. College, Sakri, Dist. Dhule (M.S), India, for providing laboratory facilities during tenure of research work and also thankful to ZSI, Pune for scientific identification of Molluscan species. REFERENCES Ahirrao KD. (2003). Effect of sevin on some ecophysiological aspects of a Melanoid snail, Melania scabra. Ph. D. Thesis submitted to Dr. BAMU, Aurangabad. Ahirrao KD and Khedkar GD. (2012). Variations in LC50 of some pesticides due to physic-chemical parameters and impact of sevin on neurosecretory cells of a fresh water snail, Thiara lineata, Journal of Research in Biology, 1:050-056. El-kady GA, Shoukry A, Reda LA, El-Badri YS. (2000). Survey and population dynamics of fresh water snail in newly settled areas of the Sinai Peninsula. Egyptian Journal of Biology, 2:42-48. Hussein MA, Obuid-Allah AH, Mahmoud AA, Fangary HM. (2011). Population dynamics of fresh water snails (Mollusca:Gastrapoda) at Qena Governorate, Upper Egypt. Egypt. Acad. J. Biol. Sci., 3 (1):11-22. Hyman LH. (1967). The invertebrates Vol.6. Mollusca, 1, McGraw Hill, New York. Micheal P. (1984). Tata McGraw – Hill Publishing Company Limited, New Delhi. Patole VM. (2010). Ecology and biodiversity of Mangroves in Mochemad estuary of Vengurla, South Konkan, Maharashtra. Ph. D. Thesis submitted to University of Mumbai. Pielou EC. (1975). Ecological diversity. Wiley, New York,165. Sharma KK. Sharma SP and Sawhney N. (2009). Distribution and ecology same freshwater molluscs of the Jammu Division of the J and K State. J. Environ. Bio -sci. 23(2):179-181. Sharma KK, Samita Chowdhary and Arti Sharma. (2010). Malacofauna diversity of river Chenab fed stream(Gho-Manhasan), Bioscan, 6(2):267-279. Subba Rao NV. (1989). Handbook: Freshwater molluscs of India. Zoological Survey of India, Calcutta. Dolikar AV, Mohite AS and Charde PN. (2014). Correlation of molluscan diversity with physico- chemical characteristic of water of Gorewada reservoir, Nagpur, India. International Journal of Life Sciences, Special issue, A2:197-202. Mohan D, Elumalai V, Subbulakshmi G, Jaylakshami S and Sriniwasan M. (2013). Biodiversity of cultivable molluscan resources from Pulicat Lake, Southeast coast of India, Arthropods 2(2): 53-65. Shannon EC and Wiener W. (1949). The Mathematical theory of communication, University of Illinois Press Urbana, 125. Simpson EH. (1949). Measurement of diversity, Nature,
  • 7. Journal of Research in Biology (2016) 6(2):1977-1983 1983 Patil et al., 2016 163:688. Preston HB. (1915). The fauna of British India including Ceylon and Burma. Mollusca (Freshwater Gastropoda and Pelecypoda). Taylor and Francis, Landon, i-xi+ 244. Tonapi GT. (1980). Freshwater animals of india. An Ecological Approach. Oxford and IBH publishing co., New Delhi, Bombay, Calcutta 341. Rao SNV. (1989): Freshwater Mollusca of India. In. Rao KS. (ED.). Recent advances in freshwater Biology. New Delhi. Anmol Publication. 2:187-202. Submit your articles online at www.jresearchbiology.com Advantages  Easy online submission  Complete Peer review  Affordable Charges  Quick processing  Extensive indexing  You retain your copyright submit@jresearchbiology.com www.jresearchbiology.com/Submit.php