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Molluscan Diversity in Mangrove Ecosystem of Uran (Raigad),
Navi Mumbai, Maharashtra, West coast of India
Prabhakar R. Pawar
Veer Wajekar Arts, Science and Commerce College, Phunde, Uran (Raigad),
Navi Mumbai - 400 702 Maharashtra, India.
E-mail: prabhakar_pawar1962@yahoo.co.in
ABSTRACT
Aim of the present study is to assess the species diversity of molluscs from mangroves of Uran because many mangroves
associated species of molluscs acts as an indicator species for mangrove. During present study, a total of 55 species of molluscs
representing 13 orders, 30 families and 39 genera were recorded from the mangroves of Uran. Of the recorded species, 69.09 %
belonged to gastropods, 23.64 % to pelecypods and 7.27 % to cephalopods. 38 species of gastropods representing 6 orders, 18
families and 25 genera, 13 species of pelecypods representing 4 orders, 8 families and 10 genera and 4 species of cephalopods
representing 3 orders, 4 families and 4 genera were recorded. Species like Telescopium telescopium, Thais carinifera, Bursa
tuberculata, Arca granosa, Placenta placenta, Merettrix meretrix, Katelysia opima, Octopus herdmani and Sepia officinalis
were common where as Chlamys singaporina, Loligo vulgaris and Amphitretus pelagicus were rare. At present, ecological
conditions in mangroves of Uran supports high density of molluscs but due to intense industrialization and urbanization,
pollution of Uran coast cannot be ignored. Therefore, data presented in this paper can be taken as a base line data.
Key Words: Mangroves, Molluscs, Navi Mumbai, Species diversity, Urbanization, Uran.
INTRODUCTION
Mangrove forests are among the world’s most productive ecosystems and cover an area of about 18
X 106 hectares [1]. Mangrove habitats harbour much of the world’s tropical biodiversity and 50% of
the world’s mangrove forests have been lost as a result of clearing and alteration of coastlines [2].
Mangroves are one of the biologically diverse ecosystems in the world, rich in organic matter and
nutrients and support very large biomass of flora and fauna [3]. Knowledge on species diversity of an
ecosystem would help maximizing resource utilization in a sustainable manner besides preserving
biodiversity [4]. With continuing degradation and destruction of mangroves, there is a critical need
to understand the biodiversity of the mangrove ecosystems [5].
The Indian mangroves cover about 4827 Km2, with about 57% of them along the east coast, 23%
along the west coast and 20% in Andaman and Nicobar Islands [6]. The total number of mangrove-
inhabiting faunal species in Indian mangroves is 3,111, which includes prawns, crabs and molluscs,
fish, fish parasites, insets, reptiles, amphibian and mammals [7]. Anthropogenic activities involving
development projects have resulted in depletion of coastal resources, destruction of mangrove
habitats, disruption of ecosystem processes and loss of biodiversity [8].
Mumbai, a major metropolis and one of the world’s most populous cities called as the Urbs Prima of
India, generates 0.85 millions m3/d of liquid effluent and 14,600 t/d of solid waste, which without
any treatment, are discharged in the coastal region in and around Mumbai [9]. Estimates of area of
mangroves in Mumbai varied from 248.7 Km2 [10] to 200 Km2 [11] to 92.94 Km2 [12] to 26.97 Km2
[13]. Zingde [14] reported that Mumbai has lost 40 % of all its mangroves in the past decade because
of overexploitation and unsustainable demand for housing, slums, sewage treatment and garbage
dumps.
Molluscs forms an important link in food chain from primary to tertiary level leading to fish
production and also an edible source for coastal population. Besides, they are utilized for ornamental
trade, pharmacological products and in the manufacture of lime and cement [15]. In India, till today,
5070 species of molluscs have been recorded of which, 3370 species are from marine habitats [16]. 8
species of oysters, 2 species of mussels, 17 species of clams, 6 species of pearl oysters, 4 species of
giant clams, 1 species of window pane oyster and other gastropods such as Sacred chank, Trochus,
Turbo as well as 15 species of cephalopods are exploited from the Indian marine region [6].
Original Article
Bulletin of Environment, Pharmacology and Life Sciences
Online ISSN 2277 – 1808
Bull. Environ. Pharmacol. Life Sci.; Volume 1 [6] May 2012: 55 - 59
© All Rights Reserved Academy for Environment and Life Sciences, India
Website: www.bepls.com
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Till now extensive scientific research on ecological aspects of molluscan fauna in mangroves has
been carried out in India however data on species diversity of molluscs in mangroves of Uran, Navi
Mumbai is not available, hence, the present study is undertaken.
MATERIALS AND METHODS
The study area:
Geographically, Uran with the population of 23,251 is located along the eastern shore of Mumbai
harbour opposite to Coloba. A creek called ‘Uran creek / Sheva creek’ (Lat. 180 50’ 20” N and Long.
720 57’ 5” E) encircles Uran city towards the north side and is continuous with the Panvel creek and
Thane creek. Creek namely Dharamtar creek (Lat.180 50' 5" N and Long. 720 57' 10" E) encircles
Uran city towards the south side and is continuous with the Karanja creek and Pen – Khopoli creek.
On the west side, Uran is encircled by Arabian Sea (Fig. 1). Both creeks have rocky shore towards the
seaward side where as remaining part of the creeks is marshy and of mud flats. Both Uran creek and
Dharamtar creek are uniformly deep with 10 meters range and have moderate cover of mangroves
with mud flats and low lying marshy areas on their sides. The coastal environment of Uran has been
under considerable stress since the onset of industries like Oil and Natural Gas Commission LPG
Distillation Plant, Grindwell Norton Ltd., MSEB Gas Turbine Power Station, Bharat Petroleum
Corporation Ltd., Jawaharlal Nehru Port Trust (JNPT), Nhava-Seva International Container Terminal
(NSICT), Container Freight Stations (CFS) etc. An international port called ‘Jawaharlal Nehru Port
Trust (JNPT)’ was established in 1989 near the Uran creek and supports a variety of maritime
activities; as a result, the area of Uran creek became the ground for hectic activities of Container
Freight Stations (CFS). These activities affect the ecology of fauna and flora of mangroves. Hence this
area has been identified for the ecological assessment.
Species diversity of molluscs in mangroves:
For present investigation, 2 study sites separated approximately by 10 km were selected along the
coastal line of Uran i. e. Sheva Creek and Dharamtar Creek. Along the selected sites where the
mangroves vegetation is present, were visited monthly from April 2009 to March 2011 for
assessment of species diversity of molluscs.
Molluscs were hand-picked from the intertidal, sub tidal as well as from the seaward fringes of the
mangroves and carried to the laboratory in icebox. Specimens were narcotized with powdered
menthol to extend fully and killed by using 1% chloral hydrate. Animals were preserved in 5%
seawater buffered formalin. For correct identification, standard keys of Menon et al [17],
Subrahmanyam et al [18], Apte [19] were followed.
RESULTS AND DISCUSSION
A total of 55 species of molluscs representing 13 orders, 30 families and 39 genera were recorded
from the mangroves of Uran coast. Of the recorded species, 69.09 % belonged to gastropods, 23.64
% to pelecypods and 7.27 % to cephalopods. The recorded species in alphabetical order of families is
given in Table 1 and 2.
38 species of gastropods representing 6 orders, 18 families and 25 genera were recorded during
present study. Among gastropods species of Telescopium telescopium, Thais carinifera and Bursa
tuberculata were recorded abundantly at both sites. Remaining species were common at both sites
throughout the period of investigation.
13 species of pelecypods representing 4 orders, 8 families and 10 genera were recorded. Species like
Arca granosa, Placenta placenta, Merettrix meretrix and Katelysia opima were common whereas
Chlamys singaporina shows rare distribution at both study sites.
4 species of cephalopods representing 3 orders, 4 families and 4 genera were recorded during
present investigation. Octopus herdmani and Sepia officinalis were common whereas Loligo vulgaris
and Amphitretus pelagicus were rare at both sites.
The coastal environment of Uran has been under considerable stress since the onset of other
industries and JNPT since 1989. Hectic activities of Container Freight Stations (CFS), urbanization,
industrialization and reclamation in the stretch of creek around Uran, result in the loss of mangrove
biodiversity. Several incidences of coastal pollution occur because of leakage/discharge of
transporting materials along with industrial effluents.
Prabhakar R. Pawar
~ 57 ~
Fig. 1: General map of study area.
Table 1: List of gastropods recorded in mangroves of Uran (Raigad), Navi Mumbai.
No. Order Family Binomial Name
1 Archaeogastropoda Trochidae Trochus stellatus (Gmelin, 1791)
2 Archaeogastropoda Trochidae Trochus radiatus (Gmelin, 1791)
3 Archaeogastropoda Trochidae Trochus tentorium Gmelin, 1791)
4 Archaeogastropoda Trochidae Euchelus asper (Gmelin, 1791)
5 Archaeogastropoda Trochidae Clancules ceylonicus (Nevill, 1869)
6 Archaeogastropoda Turbinideae Astrea stellata (Gmelin, 1791)
7 Neritimorpha Neritidae Nerita oryzarum (Recluz, 1841)
8 Neritimorpha Neritidae Nerita crepidularia (Lamarck, 1816)
9 Neritimorpha Neritidae Nerita albicilla (Linnaeus, 1758)
10 Caenogastropoda Ficidae Ficus gracilis (Sowerby, 1825)
11 Caenogastropoda Strombidae Tibia curta (Sowerby, 1842)
12 Hypsogastropoda Bursidae Bursa lissostroma (Smith, 1914)
13 Hypsogastropoda Bursidae Bursa spinosa (Lamarck, 1816)
14 Hypsogastropoda Bursidae Bursa elegans (Sowerby, 1835)
15 Hypsogastropoda Bursidae Bursa tuberculata (Brodrip, 1833)
16 Hypsogastropoda Naticidae Natica picta (Recluz, 1844)
17 Hypsogastropoda Naticidae Natica maculosa (Lam., 1799)
18 Hypsogastropoda Planaxidae Planaxis sulcatus (Born, 1778)
19 Hypsogastropoda Potamididae Telescopium telescopium (Linn., 1758)
Prabhakar R. Pawar
~ 58 ~
20 Hypsogastropoda Potamididae Potamides cingulatus (Gmelin, 1791)
21 Neogastropoda Buccinidae Babylonia spirata (Linnaeus, 1758)
22 Neogastropoda Buccinidae Cantharus spiralis (Gray, 1846)
23 Neogastropoda Cancellaridae Cancellaria costifera (Sowerby, 1835)
24 Neogastropoda Conidae Conus mutabilis (Reeve, 1844)
25 Neogastropoda Cypraeidae Erosaria lamarcki (Gray, 1825)
26 Neogastropoda Muricidae Murex adustus (Lamarck, 1799)
27 Neogastropoda Muricidae Murex tribulus (Linnaeus, 1758)
28 Neogastropoda Muricidae Murex brunneus (LinK. 1807)
29 Neogastropoda Muricidae Ocinebra bombayana (Melvill, 1893)
30 Neogastropoda Muricidae Thais carinifera (Lamarck, 1822)
31 Neogastropoda Muricidae Thais sacellum (Gmelin, 1791)
32 Neogastropoda Onchidiidae Onchidium damelii (Samper, 1882)
33 Neogastropoda Turridae Surcula javana (Linnaeus, 1758)
34 Neogastropoda Turridae Surcula amicta (Smith, 1877)
35 Neogastropoda Turridae Clavus crassa (Smith, 1888)
36 Neogastropoda Volemidae Hemifuus pugilinus (Born, 1778)
37 Neogastropoda Volemidae Hemifuus cochlidium (Linnaeus, 1758)
38 Pulmonata Siphonariidae Siphonaria laciniosa (Linn., 1758)
Table 2: List of pelecypods and cephalopods recorded in mangroves of Uran (Raigad),
Navi Mumbai.
No. Order Family Binomial Name
Pelecypods
1 Eulamellibranchiata Pectinidae Chlamys singaporina (Sowerby, 1842)
2 Ostreoida Ostreidae Placenta placenta (Linnaeus, 1758)
3 Pteriomorpha Arcidae Arca granosa (Linnaeus, 1758)
4 Veneroida Cardiidae Cardium flavum (Linnaeus, 1758)
5 Veneroida Dosiniiae Vellorita cyprinoids (Gray, 1825)
6 Veneroida Mactridae Mactre cornea (Poli, 1791)
7 Veneroida Meretricinae Merettrix meretrix (Linnaeus, 1758)
8 Veneroida Meretricinae Merettrix casta (Chemnitz, 1782)
9 Veneroida Meretricinae Merettrix lyrata (Sowerby, 1851)
10 Veneroida Veneridae Callista erycina (Linnaeus, 1758)
11 Veneroida Veneridae Dosinia cretacea (Reeve, 1850)
12 Veneroida Veneridae Dosinia gibba (H. & A. Adams, 1856)
13 Veneroida Veneridae Katelysia opima (Gmelin, 1791)
Cephalopods
1 Octopoda Amphitretidae Amphitretus pelagicus
2 Octopoda Octopodidae Octopus herdmani (Hoyle, 1904)
3 Sepiida Sepiidae Sepia officinalis (Linnaeus, 1758)
4 Teuthida Loligunidae Loligo vulgaris (Lamarck, 1798)
Disposal of domestic wastes and untreated or partially treated industrial effluents in coastal region
of Uran, Navi Mumbai have depleted coastal resources, public health risk and loss of coastal and
marine biodiversity. Sighting of dead fish surfacing in creeks of Mumbai and Navi Mumbai (Panvel
creek, Vashi creek, Belapur creek etc.) is common from last few years affecting the livelihood of
fishermen. Dumping of industrial effluents, untreated sewage and unchecked encroachment along
the coastal line have resulted in deterioration of water quality and incidences of industrial pollution
are common in creeks of Mumbai and Navi Mumbai. Slaughtering of mangroves from Navi Mumbai
region due to over exploration, unsustainable demand and reclamation have resulted in destruction
of marine life [20].
Prabhakar R. Pawar
~ 59 ~
In conclusion, it is stated that, number of molluscs recorded in mangroves of Uran indicates fairly
good health of the sediments in mangroves. Because of regular tidal flushing, the molluscan fauna
appear to be rich and healthy. In coming few years, area around Uran coast will be dominated by
intense industrialization and urbanization. In such circumstances, pollution of Uran coast cannot be
ignored. Therefore, data presented in this paper can be taken as a base line data for management of
the mangrove ecosystem of Uran in near future.
ACKNOWLEDGEMENT
Financial support provided by University Grants Commission, Western Regional Office, Pune is
gratefully acknowledged. The author wishes to express deep sense of gratitude to Prof. Dr. B. G.
Kulkarni, Director, The Institute of Science, Mumbai for encouragement and support. Special thanks
are due to Miss L. S. Patil for the critical reading of the manuscript. The author is thankful to The
Principal, Veer Wajekar Arts, Science and Commerce College, Phunde (Uran) for healthy cooperation.
REFERENCES
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2. Duke, N. C., (1992). Mangrove floristic and biogeography. In Robertson, A. I. & D. M. Alongi (Eds.), Tropical mangrove
ecosystems, (American Geophysical Union, Washington DC): 63–100.
3. Robin, L. E. and N. I. Bazelevic, 1966. The biological production of main vegetation types in the Northern Hemisphere
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4. Biju, A and G. R. Deepthi, (2009). Mean trophic index of fish fauna associated with trawl bycatch of Kerala, southwest
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Maharashtra. Electr. J. Envir.Sci., 4:113-117.
Prabhakar R. Pawar

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Molluscan diversity in mangroves of uran

  • 1. ~ 55 ~ Molluscan Diversity in Mangrove Ecosystem of Uran (Raigad), Navi Mumbai, Maharashtra, West coast of India Prabhakar R. Pawar Veer Wajekar Arts, Science and Commerce College, Phunde, Uran (Raigad), Navi Mumbai - 400 702 Maharashtra, India. E-mail: prabhakar_pawar1962@yahoo.co.in ABSTRACT Aim of the present study is to assess the species diversity of molluscs from mangroves of Uran because many mangroves associated species of molluscs acts as an indicator species for mangrove. During present study, a total of 55 species of molluscs representing 13 orders, 30 families and 39 genera were recorded from the mangroves of Uran. Of the recorded species, 69.09 % belonged to gastropods, 23.64 % to pelecypods and 7.27 % to cephalopods. 38 species of gastropods representing 6 orders, 18 families and 25 genera, 13 species of pelecypods representing 4 orders, 8 families and 10 genera and 4 species of cephalopods representing 3 orders, 4 families and 4 genera were recorded. Species like Telescopium telescopium, Thais carinifera, Bursa tuberculata, Arca granosa, Placenta placenta, Merettrix meretrix, Katelysia opima, Octopus herdmani and Sepia officinalis were common where as Chlamys singaporina, Loligo vulgaris and Amphitretus pelagicus were rare. At present, ecological conditions in mangroves of Uran supports high density of molluscs but due to intense industrialization and urbanization, pollution of Uran coast cannot be ignored. Therefore, data presented in this paper can be taken as a base line data. Key Words: Mangroves, Molluscs, Navi Mumbai, Species diversity, Urbanization, Uran. INTRODUCTION Mangrove forests are among the world’s most productive ecosystems and cover an area of about 18 X 106 hectares [1]. Mangrove habitats harbour much of the world’s tropical biodiversity and 50% of the world’s mangrove forests have been lost as a result of clearing and alteration of coastlines [2]. Mangroves are one of the biologically diverse ecosystems in the world, rich in organic matter and nutrients and support very large biomass of flora and fauna [3]. Knowledge on species diversity of an ecosystem would help maximizing resource utilization in a sustainable manner besides preserving biodiversity [4]. With continuing degradation and destruction of mangroves, there is a critical need to understand the biodiversity of the mangrove ecosystems [5]. The Indian mangroves cover about 4827 Km2, with about 57% of them along the east coast, 23% along the west coast and 20% in Andaman and Nicobar Islands [6]. The total number of mangrove- inhabiting faunal species in Indian mangroves is 3,111, which includes prawns, crabs and molluscs, fish, fish parasites, insets, reptiles, amphibian and mammals [7]. Anthropogenic activities involving development projects have resulted in depletion of coastal resources, destruction of mangrove habitats, disruption of ecosystem processes and loss of biodiversity [8]. Mumbai, a major metropolis and one of the world’s most populous cities called as the Urbs Prima of India, generates 0.85 millions m3/d of liquid effluent and 14,600 t/d of solid waste, which without any treatment, are discharged in the coastal region in and around Mumbai [9]. Estimates of area of mangroves in Mumbai varied from 248.7 Km2 [10] to 200 Km2 [11] to 92.94 Km2 [12] to 26.97 Km2 [13]. Zingde [14] reported that Mumbai has lost 40 % of all its mangroves in the past decade because of overexploitation and unsustainable demand for housing, slums, sewage treatment and garbage dumps. Molluscs forms an important link in food chain from primary to tertiary level leading to fish production and also an edible source for coastal population. Besides, they are utilized for ornamental trade, pharmacological products and in the manufacture of lime and cement [15]. In India, till today, 5070 species of molluscs have been recorded of which, 3370 species are from marine habitats [16]. 8 species of oysters, 2 species of mussels, 17 species of clams, 6 species of pearl oysters, 4 species of giant clams, 1 species of window pane oyster and other gastropods such as Sacred chank, Trochus, Turbo as well as 15 species of cephalopods are exploited from the Indian marine region [6]. Original Article Bulletin of Environment, Pharmacology and Life Sciences Online ISSN 2277 – 1808 Bull. Environ. Pharmacol. Life Sci.; Volume 1 [6] May 2012: 55 - 59 © All Rights Reserved Academy for Environment and Life Sciences, India Website: www.bepls.com
  • 2. ~ 56 ~ Till now extensive scientific research on ecological aspects of molluscan fauna in mangroves has been carried out in India however data on species diversity of molluscs in mangroves of Uran, Navi Mumbai is not available, hence, the present study is undertaken. MATERIALS AND METHODS The study area: Geographically, Uran with the population of 23,251 is located along the eastern shore of Mumbai harbour opposite to Coloba. A creek called ‘Uran creek / Sheva creek’ (Lat. 180 50’ 20” N and Long. 720 57’ 5” E) encircles Uran city towards the north side and is continuous with the Panvel creek and Thane creek. Creek namely Dharamtar creek (Lat.180 50' 5" N and Long. 720 57' 10" E) encircles Uran city towards the south side and is continuous with the Karanja creek and Pen – Khopoli creek. On the west side, Uran is encircled by Arabian Sea (Fig. 1). Both creeks have rocky shore towards the seaward side where as remaining part of the creeks is marshy and of mud flats. Both Uran creek and Dharamtar creek are uniformly deep with 10 meters range and have moderate cover of mangroves with mud flats and low lying marshy areas on their sides. The coastal environment of Uran has been under considerable stress since the onset of industries like Oil and Natural Gas Commission LPG Distillation Plant, Grindwell Norton Ltd., MSEB Gas Turbine Power Station, Bharat Petroleum Corporation Ltd., Jawaharlal Nehru Port Trust (JNPT), Nhava-Seva International Container Terminal (NSICT), Container Freight Stations (CFS) etc. An international port called ‘Jawaharlal Nehru Port Trust (JNPT)’ was established in 1989 near the Uran creek and supports a variety of maritime activities; as a result, the area of Uran creek became the ground for hectic activities of Container Freight Stations (CFS). These activities affect the ecology of fauna and flora of mangroves. Hence this area has been identified for the ecological assessment. Species diversity of molluscs in mangroves: For present investigation, 2 study sites separated approximately by 10 km were selected along the coastal line of Uran i. e. Sheva Creek and Dharamtar Creek. Along the selected sites where the mangroves vegetation is present, were visited monthly from April 2009 to March 2011 for assessment of species diversity of molluscs. Molluscs were hand-picked from the intertidal, sub tidal as well as from the seaward fringes of the mangroves and carried to the laboratory in icebox. Specimens were narcotized with powdered menthol to extend fully and killed by using 1% chloral hydrate. Animals were preserved in 5% seawater buffered formalin. For correct identification, standard keys of Menon et al [17], Subrahmanyam et al [18], Apte [19] were followed. RESULTS AND DISCUSSION A total of 55 species of molluscs representing 13 orders, 30 families and 39 genera were recorded from the mangroves of Uran coast. Of the recorded species, 69.09 % belonged to gastropods, 23.64 % to pelecypods and 7.27 % to cephalopods. The recorded species in alphabetical order of families is given in Table 1 and 2. 38 species of gastropods representing 6 orders, 18 families and 25 genera were recorded during present study. Among gastropods species of Telescopium telescopium, Thais carinifera and Bursa tuberculata were recorded abundantly at both sites. Remaining species were common at both sites throughout the period of investigation. 13 species of pelecypods representing 4 orders, 8 families and 10 genera were recorded. Species like Arca granosa, Placenta placenta, Merettrix meretrix and Katelysia opima were common whereas Chlamys singaporina shows rare distribution at both study sites. 4 species of cephalopods representing 3 orders, 4 families and 4 genera were recorded during present investigation. Octopus herdmani and Sepia officinalis were common whereas Loligo vulgaris and Amphitretus pelagicus were rare at both sites. The coastal environment of Uran has been under considerable stress since the onset of other industries and JNPT since 1989. Hectic activities of Container Freight Stations (CFS), urbanization, industrialization and reclamation in the stretch of creek around Uran, result in the loss of mangrove biodiversity. Several incidences of coastal pollution occur because of leakage/discharge of transporting materials along with industrial effluents. Prabhakar R. Pawar
  • 3. ~ 57 ~ Fig. 1: General map of study area. Table 1: List of gastropods recorded in mangroves of Uran (Raigad), Navi Mumbai. No. Order Family Binomial Name 1 Archaeogastropoda Trochidae Trochus stellatus (Gmelin, 1791) 2 Archaeogastropoda Trochidae Trochus radiatus (Gmelin, 1791) 3 Archaeogastropoda Trochidae Trochus tentorium Gmelin, 1791) 4 Archaeogastropoda Trochidae Euchelus asper (Gmelin, 1791) 5 Archaeogastropoda Trochidae Clancules ceylonicus (Nevill, 1869) 6 Archaeogastropoda Turbinideae Astrea stellata (Gmelin, 1791) 7 Neritimorpha Neritidae Nerita oryzarum (Recluz, 1841) 8 Neritimorpha Neritidae Nerita crepidularia (Lamarck, 1816) 9 Neritimorpha Neritidae Nerita albicilla (Linnaeus, 1758) 10 Caenogastropoda Ficidae Ficus gracilis (Sowerby, 1825) 11 Caenogastropoda Strombidae Tibia curta (Sowerby, 1842) 12 Hypsogastropoda Bursidae Bursa lissostroma (Smith, 1914) 13 Hypsogastropoda Bursidae Bursa spinosa (Lamarck, 1816) 14 Hypsogastropoda Bursidae Bursa elegans (Sowerby, 1835) 15 Hypsogastropoda Bursidae Bursa tuberculata (Brodrip, 1833) 16 Hypsogastropoda Naticidae Natica picta (Recluz, 1844) 17 Hypsogastropoda Naticidae Natica maculosa (Lam., 1799) 18 Hypsogastropoda Planaxidae Planaxis sulcatus (Born, 1778) 19 Hypsogastropoda Potamididae Telescopium telescopium (Linn., 1758) Prabhakar R. Pawar
  • 4. ~ 58 ~ 20 Hypsogastropoda Potamididae Potamides cingulatus (Gmelin, 1791) 21 Neogastropoda Buccinidae Babylonia spirata (Linnaeus, 1758) 22 Neogastropoda Buccinidae Cantharus spiralis (Gray, 1846) 23 Neogastropoda Cancellaridae Cancellaria costifera (Sowerby, 1835) 24 Neogastropoda Conidae Conus mutabilis (Reeve, 1844) 25 Neogastropoda Cypraeidae Erosaria lamarcki (Gray, 1825) 26 Neogastropoda Muricidae Murex adustus (Lamarck, 1799) 27 Neogastropoda Muricidae Murex tribulus (Linnaeus, 1758) 28 Neogastropoda Muricidae Murex brunneus (LinK. 1807) 29 Neogastropoda Muricidae Ocinebra bombayana (Melvill, 1893) 30 Neogastropoda Muricidae Thais carinifera (Lamarck, 1822) 31 Neogastropoda Muricidae Thais sacellum (Gmelin, 1791) 32 Neogastropoda Onchidiidae Onchidium damelii (Samper, 1882) 33 Neogastropoda Turridae Surcula javana (Linnaeus, 1758) 34 Neogastropoda Turridae Surcula amicta (Smith, 1877) 35 Neogastropoda Turridae Clavus crassa (Smith, 1888) 36 Neogastropoda Volemidae Hemifuus pugilinus (Born, 1778) 37 Neogastropoda Volemidae Hemifuus cochlidium (Linnaeus, 1758) 38 Pulmonata Siphonariidae Siphonaria laciniosa (Linn., 1758) Table 2: List of pelecypods and cephalopods recorded in mangroves of Uran (Raigad), Navi Mumbai. No. Order Family Binomial Name Pelecypods 1 Eulamellibranchiata Pectinidae Chlamys singaporina (Sowerby, 1842) 2 Ostreoida Ostreidae Placenta placenta (Linnaeus, 1758) 3 Pteriomorpha Arcidae Arca granosa (Linnaeus, 1758) 4 Veneroida Cardiidae Cardium flavum (Linnaeus, 1758) 5 Veneroida Dosiniiae Vellorita cyprinoids (Gray, 1825) 6 Veneroida Mactridae Mactre cornea (Poli, 1791) 7 Veneroida Meretricinae Merettrix meretrix (Linnaeus, 1758) 8 Veneroida Meretricinae Merettrix casta (Chemnitz, 1782) 9 Veneroida Meretricinae Merettrix lyrata (Sowerby, 1851) 10 Veneroida Veneridae Callista erycina (Linnaeus, 1758) 11 Veneroida Veneridae Dosinia cretacea (Reeve, 1850) 12 Veneroida Veneridae Dosinia gibba (H. & A. Adams, 1856) 13 Veneroida Veneridae Katelysia opima (Gmelin, 1791) Cephalopods 1 Octopoda Amphitretidae Amphitretus pelagicus 2 Octopoda Octopodidae Octopus herdmani (Hoyle, 1904) 3 Sepiida Sepiidae Sepia officinalis (Linnaeus, 1758) 4 Teuthida Loligunidae Loligo vulgaris (Lamarck, 1798) Disposal of domestic wastes and untreated or partially treated industrial effluents in coastal region of Uran, Navi Mumbai have depleted coastal resources, public health risk and loss of coastal and marine biodiversity. Sighting of dead fish surfacing in creeks of Mumbai and Navi Mumbai (Panvel creek, Vashi creek, Belapur creek etc.) is common from last few years affecting the livelihood of fishermen. Dumping of industrial effluents, untreated sewage and unchecked encroachment along the coastal line have resulted in deterioration of water quality and incidences of industrial pollution are common in creeks of Mumbai and Navi Mumbai. Slaughtering of mangroves from Navi Mumbai region due to over exploration, unsustainable demand and reclamation have resulted in destruction of marine life [20]. Prabhakar R. Pawar
  • 5. ~ 59 ~ In conclusion, it is stated that, number of molluscs recorded in mangroves of Uran indicates fairly good health of the sediments in mangroves. Because of regular tidal flushing, the molluscan fauna appear to be rich and healthy. In coming few years, area around Uran coast will be dominated by intense industrialization and urbanization. In such circumstances, pollution of Uran coast cannot be ignored. Therefore, data presented in this paper can be taken as a base line data for management of the mangrove ecosystem of Uran in near future. ACKNOWLEDGEMENT Financial support provided by University Grants Commission, Western Regional Office, Pune is gratefully acknowledged. The author wishes to express deep sense of gratitude to Prof. Dr. B. G. Kulkarni, Director, The Institute of Science, Mumbai for encouragement and support. Special thanks are due to Miss L. S. Patil for the critical reading of the manuscript. The author is thankful to The Principal, Veer Wajekar Arts, Science and Commerce College, Phunde (Uran) for healthy cooperation. REFERENCES 1. Spalding, M. D., F. Blasco and C. D. Field, (1997). World mangrove atlas, (The International Society for Mangrove Ecosystems, Okinawa, Japan), pp. 178. 2. Duke, N. C., (1992). Mangrove floristic and biogeography. In Robertson, A. I. & D. M. Alongi (Eds.), Tropical mangrove ecosystems, (American Geophysical Union, Washington DC): 63–100. 3. Robin, L. E. and N. I. Bazelevic, 1966. The biological production of main vegetation types in the Northern Hemisphere of the Old World. For abs., 27: 369–372. 4. Biju, A and G. R. Deepthi, (2009). Mean trophic index of fish fauna associated with trawl bycatch of Kerala, southwest coast of India. J. Mar. Biol. Ass. India, 51(2): 145–157. 5. Vannucci, M., 2002. Indo-west Pacific mangroves, In Lacerda L. D. (Eds.) Mangrove ecosystems, (Springer, Berlin), : 122 – 215. 6. Venkataraman, K. and M. Wafar, (2005). Coastal and marine biodiversity of India. Ind. J. Mar. Sci., 34(1): 57-75. 7. Kathiresan, K. and S. Z. Qasim, (2005). Biodiversity in mangrove ecosystems. Hindustan Publishers, New Delhi. 8. Vijay, V., R. S. Birader, A. B. Inamdar, G. Deshmukhe, S. Baji and M. Pikle, (2005). Mangrove mapping and change detection around Mumbai (Bombay) using remotely sensed data. Indian Journal of Marine Sciences, 34(3): 310–315. 9. Zingde, M. D., (1999). Marine environmental status and coastal zone management issues in India. In: South Asia Regional Workshop on Estuarine modeling and Coastal Zone Management. A Joint START / LOICZ / IGBP-SL Workshop, Apr. 28–30, Colombo, Sri Lanka. pp. 153–164. 10. Queshi, I. M., (1957). Botanical silviculture features of mangrove forest of Bombay State. Proceeding of Mangrove Symposium (Government of India Press, Calcutta), pp. 20–26. 11. Blasco, F., C. Caratini, S. Chanda and G. Thanikaimoni, (1975). Main characteristics of Indian mangroves. Proceeding of the International Symposium on Biology and Management of Mangroves, (Walsh, G. E., S. G. Snedkar and H. J. Reas ed.) IFAS University of Florida:71–87. 12. Inamdar, A. B., R. K. Surendrakumar, M. C. Behera, H. B. Chauhan and S. Nayak, (2000). Land use mapping of Maharashtra Coastal Regulatory Zone, SAC/RESA/MWRD/CRZ/SN/02/00 (Indian Space Research Organization, Ahmadabad, India): pp 42. 13. Mukherji, M., (2002). Degradation of creeks and mangroves and its impact on urban environment – A case study of Mumbai. Proceeding of National Seminar on Creeks, Estuaries and Mangroves – Pollution and Conservation. B. N. B. College of Science, Thane, Mumbai, Nov.28–30, pp 331–333. 14. Zingde, M. D., (2002). Degradation of Marine habitats and Coastal management framework. Proceeding of National Seminar on Creeks, Estuaries and Mangroves – Pollution and Conservation. B. N. B. College of Science, Thane, Mumbai, Nov.28–30, pp 3–7. 15. Jaiswar, A. K. and B. G. Kulkarni, (2005). Conservation of Molluscan biodiversity from intertidal area of Mumbai coast. J. Natcon, 17(1): 93–105. 16. Subba Rao, N. V., (1991). Mollusca in Animal Resources of India (Zoological Survey of India, Calcutta): 125–147. 17. Menon, P. K. B., A. K. Datta and D. Das Gupta, (1951). On the marine fauna of Gulf of Kutch Part II – Gastropoda. J. Bombay Nat. Hist. Soc. 8(2): 475–494. 18. Subrahmanyam, T. V., K. R. Karandikar and N. N. Murti, 1949. The marine Pelecypoda of Bombay. J. Univ. of Bombay, 17: 50–81. 19. Apte, D. A., (1988). The book of Indian shells. Bombay Natural History Society, Oxford University Press, India pp 115. 20. Pawar, P. R., (2011). Floral diversity of mangrove ecosystem from coastal environment of Uran (Raigad), Maharashtra. Electr. J. Envir.Sci., 4:113-117. Prabhakar R. Pawar