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Int. J. Life. Sci. Scienti. Res., 3(3): 995-1002 MAY 2017
Copyright © 2015-2017| IJLSSR by Society for Scientific Research is under a CC BY-NC 4.0 International License Page 995
Diversity of Halophytes in Gulf of Kachchh,
Gujarat
Harshad Salvi1
, Lopamudra Das2
*, Bhargav Brahmbhatt3
, Nilesh Vaghela4
, R.D. Kamboj5
1
Scientist, GEER Foundation, Gandhinagar, Gujarat, India
2
Research Associate, GEER Foundation, Gandhinagar, Gujarat, India
3, 4
Ex- Senior Research Fellow, GEER Foundation, Gandhinagar, Gujarat, India
5
Additional Principal, Chief Conservator of Forest and Director, GEER Foundation, Gandhinagar, Gujarat, India
*
Address for Correspondence: Dr. Lopamudra Das, Research Associate, GEER Foundation,
Gandhinagar, Gujarat, India
Received: 03 February 2017/Revised: 04 March 2017/Accepted: 12 April 2017
ABSTRACT- Floristic inventory and diversity assessment are necessary to understand the present diversity status of the
conservation of biodiversity. Shorelines are one of the most rapidly changing places on the Earth. The Gulf of Kachchh
(GoK) is a semi-enclosed coastal indentation with predominance of mangrove ecosystems, coral reefs, associated rich
marine diversity and coastal terrestrial vegetation. Halophytes are flowering plants, which are naturally found in saline
habitats such as coastal swamps, coastal dunes, inland salt flats etc. Present works reveals the diversity of halophytes in
GoK. Total 27 halophytes were encountered from 13 coastal talukas and islands of GoK. Islands of GoK, and Bhachau
taluka are the area with highest diversity in GoK. In the present study α diversity (Shannon diversity index, Simpson's
Index, species richness, evenness index) of the halophyte community was studied. From the study of biodiversity it was
observed that highest species diversity (Shannon-Wiener diversity H’) was observed in Jamnagar district and its islands
whereas species richness index (d) was highest in Devbhumi Dwarka district and its islands. Evenness index (e) was
highest (0.528) in Morbi district.
Key-words- Halophytes, Gulf of Kachchh, α-Diversity, Saline habitats
INTRODUCTION
The Gujarat state is situated on the north-western parts of
India. It (20° 2´ - 24° 41´ N latitude and 68° 8´- 74° 23´ E
longitude) occupies an area of 1,96,024 sq.km and has
1663-km-long coastline, which spreads along 13 coastal
districts and one Union Territory of Diu between Kachchh
and Valsad. Interestingly, 1663-km-long sea coast of
Gujarat is characterized by typical salt marshes (~796-km),
sand dunes (~440-km) and rocky shore (~319-km) [1]. It is
widely accepted now that among the various biodiversity
regions, the coastal and marine ecosystems are of particular
importance in terms of their utility to the human livelihood
security. Salt marshes are defined as natural or semi-natural
terrestrial halophytic- ecosystems [2]. The dominant flora is
composed of halophytic plant such as, grasses, shrub and
herbs. Salt marshes are those areas, which are periodically
inundated by the sea and which contain true halophytic
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DOI: 10.21276/ijlssr.2017.3.3.6
and salt tolerant plants occupying an area (approximate)
between the mean high water neap tide and mean high
water spring tide [3].
In the last 70 years various attempts have been made to
classify halophytes [4]. However, the simplest and clearest
definition is probably stating that “halophytes species are
those occurring in naturally saline conditions only” [5].
Halophyte plants complete their life cycle in saline habitats
with unique morphological, biological and physiological
characters, which distinguish them from sea grasses and
mangroves. There are a few hundred halophytic plant
species recorded in the world. Although voluminous
information is available on general biology and
eco-physiology of halophytes, only a few reports are
available on diversity of this fascinating group of coastal
flora [6]. Halophytes are plants of significant economic
potential which can contribute tremendously toward the
environmental restoration and also have industrial
applications in the form of essential oils, medicinal,
alcohol, fiber, latex, pulp, cosmetics etc.
Present investigations have been carried out to assess the
distribution of halophytes diversity in 13 coastal talukas
and islands of GoK.
ARTICLERESEARCH
Int. J. Life. Sci. Scienti. Res., 3(3) MAY 2017
Copyright © 2015-2017| IJLSSR by Society for Scientific Research is under a CC BY-NC 4.0 International License Page 996
MATERIALS AND METHODS
Study Area
An assessment of halophytes flora was conducted along the
GoK coast in 2011 to 2014 under Integrated Coastal Zone
Management Project. The study area consisted of 4 districts
(13 coastal talukas i.e. from Okha to Abdasa) surrounding
the Gulf of Kachchh (22° 15’ N to 23° 50’ N and 68° 20’ E
to 68° 54’ E) and its islands (Fig. 1). For the purpose of
data collection the entire study area was categorized into
four zones based on the district boundaries i.e. Devbhumi
Dwarka, Jamnagar, Morbi and Kachchh.
Fig 1: Study Area GoK
Methodology
For the present study random sampling method was
followed. In the coastal areas, line transects of 500 m were
laid perpendicular to HTL (High Tide Line) to landward
side by using 5x5 Km grid maps of Land use/Land cover
maps (Like forest, grasslands, scrublands etc.). Distance of
5 km. between two subsequent line intersects was
maintained using Global Positioning System. Within each
transect, quadrates were laid at the interval of 20 m for
Trees and Shrubs 5m ×5m and for herbs, grasses, climbers
1m×1m [7-9]. To enrich the species inventory the
opportunistic coastal area at each site (areas falling out side
of the quadrates) were also explored and observed species
were recorded and photographed.
Collection of plant specimens was carried out to know
more information on habitat and for preparation of
herbarium specimens. The species were identified using
published literature and different Floras [10-13].
Analysis of Bio-diversity: To measure α-biodiversity, it
is necessary to measure specie richness, species diversity
and the evenness of the species. Species richness is another
good aspect for measuring biodiversity.
Shannon Wiener diversity index: The Shannon
diversity index sampling measure was utilised to randomly
measure the individuals from an ‘indefinitely large’ (that is
effectively infinite) population [14]. Species diversity was
calculated using the equation [15].
H= -Ʃ pi ln pi
Where, H’= Shannon index of general diversity,
pi= the proportion abundance of the ith
species= (ni/N),
ni= The number of individuals in the ith
species and
N= The total number of individuals.
Simpson’s index: The index of dominance of the
community was calculated by Simpson’s index [16] as:
c=Ʃni (ni (ni-1)/ N (N-1)
Where c= Index of dominance, ni and N being the same as
Shannon index of general diversity.
Species richness index: Species richness S is the
simplest measure of biodiversity and is simply a count of
the number of different species in a given area. The index
of species richness (d) was calculated by following [17]
formula as-
d = (S - 1) / ln N
Where d = Margalef Diversity Index, S = Total number of
species, N = Total number of individuals
Evenness (equitability) index: The evenness
(equitability) index of the community was calculated
equation [18] as follows:
E= H’/ In S
Where H’= Shannon index and S- Number of species
RESULTS AND DISCUSSION
A total of species of 27 halophytes belonging to 23 genera
and 14 families were encountered from GoK. Halophytes
diversity includes 22 Dicot and 5 Monocot species.
Among 13 talukas and Islands of GoK, the highest number
(21) of halophyte species diversity was found in Islands of
GoK and Bhachau taluka (20) followed by Mundra, Anjar
and Khambaliya Talukas. The lowest numbers of halophyte
species were observed in Lalpur Taluka (11)
(Fig. 2 to Fig. 3).
Int. J. Life. Sci. Scienti. Res., 3(3) MAY 2017
Copyright © 2015-2017| IJLSSR by Society for Scientific Research is under a CC BY-NC 4.0 International License Page 997
Fig 2: Taluka and Island wise Species richness of Halophytes in GoK
Fig 3: Showing distribution pattern of Halophytes in the GoK (2011 - 2014)
It is widely accepted that biodiversity of coastal flora is
dependent on hydrological regime, geological and climatic
conditions [19]. Although hydrology whether it is
frequency of inundation or water source was the most
important factor, remaining criteria such as, wetland
morphology, vegetation type and geological locations were
equally important for managing coastal ecosystem [20]. In
the present study, Islands of GoK surrounded by sea water
and having high saline habitat appear to support maximum
halophytes diversity. However, the lowest diversity of
halophytes was observed in Lalpur taluka, which has less
saline area as compared to other talukas surrounding the
GoK.
The 36 species of halophytes were reported from India in
the “book Monograph on Indian Halophytes” [13]. Present
study reported 27 species of halophytes from GoK
(Gujarat), among them two species viz. Haloxylon
recurvum Bunge ex Boiss. and Zygophyllum simplex L., are
not reported in the above said book [13]. Zygophyllum
simplex L. was reported as halophyte in the book
“Halophytes as a resource for livestock and for
rehabilitation of degraded lands” [21]. H. recurvum Bunge
ex Boiss. and Z. simplex was reported as Indian desert
halophytes in the book “Contributions to the ecology of
halophytes” [22]. Thus these two species were incorporated
as halophytes in the present study.
Int. J. Life. Sci. Scienti. Res., 3(3) MAY 2017
Copyright © 2015-2017| IJLSSR by Society for Scientific Research is under a CC BY-NC 4.0 International License Page 998
Similarity among the Talukas of GoK based on halophytes species distribution through Bray Curties
similarity measure
Considering the occurrence of the halophyte species and its composition, of Jamnagar, Jodiya, Kalyanpur, Maliya and
Mandvi talukas were found to have highest similarity with each other i.e. 94%. Species composition of Okhamandal
taluka showed 92% similarity of halophytes composition with Kalyanpur, Jamnagar and Jodiya taluka. The detailed
similarity among the studied areas is given in Fig 4.
Fig 4: Similarity among the Talukas of GoK based on halophytes species
Halophytes Diversity in GoK
Calculating biodiversity is a large part of determining the
health of an ecosystem. The Shannon-Wiener Index (H’)
and Simpson’s index (c) were used to determine which
community is more diverse. The Simpson’s Index (c)
employs data regarding the proportion of the species while
the Shannon-Wiener Index (H’) includes information on
species evenness and richness. These indices take
quantitative numbers and express them into qualitative
terms.
Shannon-Wiener diversity index preferred over other
diversity indices and its values vary between 0.0-5.0 [23].
Results between 1.5 to 3.5 are indicative of normal
biological system and the index value exceeding 4.5 are
rare. Values above 3.0 indicate that the structure of habitat
is stable and balanced, while the values under 1.0 suggest
that habitat structure is being seriously degraded by many
factors such as climate change, anthropogenic pressure and
pollution. From the present biodiversity study it was
observed that the highest species diversity
(Shannon-Wiener diversity) was observed in Jamnagar
district and its islands (1.859) followed by Devbhumi
Dwarka district and its islands (1.817), Morbi district
(1.664) and Kachchh district (1.633) (Table 1). Thus the
coastal areas of GoK has been revealing Shannon- Wiener
diversity index in between 1.6 to 1.8, which indicate
normal biological system and there is no degradation of
habitat structure.
The Simpson’s Index measures the probability that two
individuals chosen at random will be the same species.
Because of this, the range for the Simpson’s Index (c) is
from Zero to One. Zero is the least diverse and one is the
highest level of diversity attainable with this index [24].
From Simpson's index (c) it was observed that Jamnagar
district and its islands (0.804) are highly diverse followed
by Devbhumi Dwarka district and its islands (0.786), Morbi
district (0.754) and Kachchh district (0.747) (Table 1).
The study came with index of dominance of 0.252 for
Kachchh district, 0.245 for Morbi district, 0.214 for
Devbhumi Dwarka district and 0.196 for Jamnagar district
(Table 1). It was reported that greater the value of index of
dominance the lower the species diversity and vice versa in
the scale of 0 to 1 [25]. Thus as highest index of dominance
was observed in Kachchh district, the diversity is lowest in
that region. Lowest index of dominance was observed in
Jamnagar district and its islands thus the diversity was
highest in that region.
Since heterogeneity contains two separate ideas- species
richness and evenness- it was only natural to try to measure
the evenness component separately [26-27]. Evenness
describes how equally individuals are distributed amongst
the species. Pielou’s evenness index (e) was highest (0.528)
in Morbi district followed by Jamnagar district and its
islands (0.494), Devbhumi Dwarka district and its islands
(0.0.647) and Kachchh district (0.365) (Table 1).
Margalef species richness index (d) was highest in
Devbhumi Dwarka district and its islands (1.519) followed
by Kachchh district (1.373), Jamnagar district and its
islands (1.262) and Morbi district (1.085) (Table 1).
Int. J. Life. Sci. Scienti. Res., 3(3) MAY 2017
Copyright © 2015-2017| IJLSSR by Society for Scientific Research is under a CC BY-NC 4.0 International License Page 999
Table 2: Checklist of Halophytes
Botanical Names / Sites 1 2 3 4 5 6 7 8 9 10 11 12 13 14
Aeluropus lagopoides (L.) Thwaites √ √ √ √ √ √ √ √ √ √ √ √ √ √
Arthrocnemum indicum (Willd.) Moq. √ × × × × × × × × × × × × ×
Artiplex stocksii(Wt.) Boiss. × √ × × × × × × × × × × × √
Cressa cretica L. √ √ √ √ √ √ √ √ √ √ √ √ √ √
Cyperus conglomeratus Rottb. √ √ √ √ √ √ √ √ × × √ √ √ √
Halopyrum mucronatum (L.) Stapf √ √ √ × √ √ √ × × √ √ √ √ √
Haloxylon recurvum Bunge ex Boiss. × × √ × √ √ √ × × √ √ √ √ √
Haloxylon salicornicum (Moq.) Bunge ex Boiss. √ √ √ √ √ √ √ × × √ √ √ √ √
Heliotropium curassavica L. × × √ × √ √ √ √ √ √ √ × √ √
Ipomoea pes-caprae (L.) R. Br. √ √ √ √ √ √ √ √ √ √ √ √ × √
Juncus maritimus Lam. × × × × × × √ √ × × × × √ √
Limonium stocksii Kuntze × × × × × × × √ × × × √ × √
Lotus garcini DC. √ × × × × × × √ × × × √ × ×
Prosopis juliflora (Sw.) DC. √ √ √ √ √ √ √ √ √ √ × √ √ √
Salicornia brachiata Miq. × × √ × √ √ √ √ × √ × × √ √
Salvadora persica L. √ √ √ √ √ √ √ √ √ √ √ √ √ √
Sericostoma pauciflorum Stocks ex. Wight √ √ √ √ × × × × × √ √ × × √
Sesuvium portulacastrum (L.) L. √ √ √ √ √ √ √ √ √ √ √ √ √ √
Sporobolus maderaspatanus Bor √ √ √ √ √ √ √ √ √ √ √ √ √ √
Suaeda fruticosa Forssk. ex. J.F.Gmel. √ √ √ √ √ √ √ √ √ √ √ √ √ √
Suaeda nudiflora Moq. √ √ √ √ √ √ √ √ √ √ √ √ √ √
Tamarix dioica Roxb. × √ √ √ √ × × × × √ √ √ √ √
Tamarix stricta Boiss. × × √ × × √ × √ × × × × × ×
Trianthema portulacastrum L. × √ × √ × × × × × × × √ × ×
Trianthema triquetra Rottler & Willd. × √ × × × × × √ × × × × × ×
Urochondra setulosa (Trin.) C.E.Hubb. √ √ √ √ √ √ √ √ √ √ √ √ √ √
Zygophyllum simplex L. × × √ × × × × × × × × × × ×
Total 16 18 20 15 17 17 17 18 11 17 17 18 17 21
Abadasa (1), Anjar (2), Bhachau (3), Gandhidham (4), Jamnagar(5), Jodiya(6), Kalyanpur (7), Khambhaliya (8), Lalpur (9), Maliya (10),
Mandvi (11), Mundra (12), Okhamandal (13), Island (14), √=Present, ×= Absent
Table 1: Various diversity indices of Halophytes in GoK
Diversity indices
Devbhumi Dwarka
District and its islands
Jamnagar
District and its
islands
Morbi
District
Kachchh District
Shannon-Wiener index (H') 1.817 1.859 1.664 1.633
Simpson's index (c ) 0.786 0.804 0.754 0.747
Dominance (1/c) 0.214 0.196 0.245 0.252
Evenness index (e) 0.410 0.494 0.528 0.365
Species richness (d) 1.519 1.262 1.085 1.373
Int. J. Life. Sci. Scienti. Res., 3(3) MAY 2017
Copyright © 2015-2017| IJLSSR by Society for Scientific Research is under a CC BY-NC 4.0 International License Page 1000
Int. J. Life. Sci. Scienti. Res., 3(3) MAY 2017
Copyright © 2015-2017| IJLSSR by Society for Scientific Research is under a CC BY-NC 4.0 International License Page 1001
Fig 5: Twenty-seven Halophyte plants species of Gulf of Kachchh (GoK) showed in Plate I and II Photographs
Int. J. Life. Sci. Scienti. Res., 3(3) MAY 2017
Copyright © 2015-2017| IJLSSR by Society for Scientific Research is under a CC BY-NC 4.0 International License Page 1002
CONCLUSIONS
The GoK is very rich in floral diversity. The present study
reveals the presence of a total 27 species of halophytes.
Diversity of halophyte plants community is highly valued
now, since these ecosystems are being increasingly
threatened by the current environmental crisis. The coastal
area and islands of GoK have shown that the halophytes
diversity is medium and indicate that the habitat structure
showing normal biological system and there is no
degradation of habitat structure. The present study will
serve as a primary input towards monitoring and sustaining
the phyto-diversity of halophytes in the coastal areas of
GoK. Study on floristic distribution and diversity of
halophytes will be useful to the conservation researchers,
scientists and coastal zone managers for effective
management of the coastal ecosystem of GoK.
ACKNOWLEDGMENT
The authors would like to thank GEER Foundation for
giving the platform to carry out the research work. We
would like to acknowledge other staff of the Foundation for
field data collection and preparation of Maps. Thanks are
also due to Department of Forests, Government of Gujarat
and Marine National Park & Sanctuary for providing the
permission to carry out this research. Authors are highly
grateful to the World Bank, MoEF & CC, NPMU-SICOM,
and SPMU-GEC for providing the financial assistance for
this project under the Integrated Coastal Zone
Management.
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[6] Lepping, O. and Daniels, F. J. A., Phytosociology of beach
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[10]Shah, G. L., Flora of Gujarat State. Vol. I & II. Sardar Patel
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[11]Cooke, T., The Flora of the Presidency of Bombay, Taylon &
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[12]eHALOPH: http://www.sussex.ac.uk/affiliates/halophytes/
/index.php, The University of Sussex.
[13]Joshi, A. J., Monograph on Indian Halophytes. Ocean &
Atmospheric Science and Technology Cell. Dept. of Life
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[15]Margalef R., Perspectives in Ecological Theory. University
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Modeling: One + Two 2009, 2(1), pp.1-14
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[26]Lloyd, M. & Ghelardi, R.J., A table for calculating the
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International Journal of Life-Sciences Scientific Research (IJLSSR)
Open Access Policy
Authors/Contributors are responsible for originality, contents, correct
references, and ethical issues.
IJLSSR publishes all articles under Creative Commons
Attribution- Non-Commercial 4.0 International License (CC BY-NC).
https://creativecommons.org/licenses/by-nc/4.0/legalcode
How to cite this article:
Salvi H, Das L, Brahmbhatt B, Vaghela N, Kamboj RD: Diversity of Halophytes in Gulf of Kachchh, Gujarat. Int. J.
Life. Sci. Scienti. Res., 2017; 3(3): 995-1002. DOI:10.21276/ijlssr.2017.3.3.6
Source of Financial Support: The World Bank, Conflict of interest: Nil

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Diversity of Halophytes in Gulf of Kachchh, Gujarat

  • 1. Int. J. Life. Sci. Scienti. Res., 3(3): 995-1002 MAY 2017 Copyright © 2015-2017| IJLSSR by Society for Scientific Research is under a CC BY-NC 4.0 International License Page 995 Diversity of Halophytes in Gulf of Kachchh, Gujarat Harshad Salvi1 , Lopamudra Das2 *, Bhargav Brahmbhatt3 , Nilesh Vaghela4 , R.D. Kamboj5 1 Scientist, GEER Foundation, Gandhinagar, Gujarat, India 2 Research Associate, GEER Foundation, Gandhinagar, Gujarat, India 3, 4 Ex- Senior Research Fellow, GEER Foundation, Gandhinagar, Gujarat, India 5 Additional Principal, Chief Conservator of Forest and Director, GEER Foundation, Gandhinagar, Gujarat, India * Address for Correspondence: Dr. Lopamudra Das, Research Associate, GEER Foundation, Gandhinagar, Gujarat, India Received: 03 February 2017/Revised: 04 March 2017/Accepted: 12 April 2017 ABSTRACT- Floristic inventory and diversity assessment are necessary to understand the present diversity status of the conservation of biodiversity. Shorelines are one of the most rapidly changing places on the Earth. The Gulf of Kachchh (GoK) is a semi-enclosed coastal indentation with predominance of mangrove ecosystems, coral reefs, associated rich marine diversity and coastal terrestrial vegetation. Halophytes are flowering plants, which are naturally found in saline habitats such as coastal swamps, coastal dunes, inland salt flats etc. Present works reveals the diversity of halophytes in GoK. Total 27 halophytes were encountered from 13 coastal talukas and islands of GoK. Islands of GoK, and Bhachau taluka are the area with highest diversity in GoK. In the present study α diversity (Shannon diversity index, Simpson's Index, species richness, evenness index) of the halophyte community was studied. From the study of biodiversity it was observed that highest species diversity (Shannon-Wiener diversity H’) was observed in Jamnagar district and its islands whereas species richness index (d) was highest in Devbhumi Dwarka district and its islands. Evenness index (e) was highest (0.528) in Morbi district. Key-words- Halophytes, Gulf of Kachchh, α-Diversity, Saline habitats INTRODUCTION The Gujarat state is situated on the north-western parts of India. It (20° 2´ - 24° 41´ N latitude and 68° 8´- 74° 23´ E longitude) occupies an area of 1,96,024 sq.km and has 1663-km-long coastline, which spreads along 13 coastal districts and one Union Territory of Diu between Kachchh and Valsad. Interestingly, 1663-km-long sea coast of Gujarat is characterized by typical salt marshes (~796-km), sand dunes (~440-km) and rocky shore (~319-km) [1]. It is widely accepted now that among the various biodiversity regions, the coastal and marine ecosystems are of particular importance in terms of their utility to the human livelihood security. Salt marshes are defined as natural or semi-natural terrestrial halophytic- ecosystems [2]. The dominant flora is composed of halophytic plant such as, grasses, shrub and herbs. Salt marshes are those areas, which are periodically inundated by the sea and which contain true halophytic Access this article online Quick Response Code Website: www.ijlssr.com DOI: 10.21276/ijlssr.2017.3.3.6 and salt tolerant plants occupying an area (approximate) between the mean high water neap tide and mean high water spring tide [3]. In the last 70 years various attempts have been made to classify halophytes [4]. However, the simplest and clearest definition is probably stating that “halophytes species are those occurring in naturally saline conditions only” [5]. Halophyte plants complete their life cycle in saline habitats with unique morphological, biological and physiological characters, which distinguish them from sea grasses and mangroves. There are a few hundred halophytic plant species recorded in the world. Although voluminous information is available on general biology and eco-physiology of halophytes, only a few reports are available on diversity of this fascinating group of coastal flora [6]. Halophytes are plants of significant economic potential which can contribute tremendously toward the environmental restoration and also have industrial applications in the form of essential oils, medicinal, alcohol, fiber, latex, pulp, cosmetics etc. Present investigations have been carried out to assess the distribution of halophytes diversity in 13 coastal talukas and islands of GoK. ARTICLERESEARCH
  • 2. Int. J. Life. Sci. Scienti. Res., 3(3) MAY 2017 Copyright © 2015-2017| IJLSSR by Society for Scientific Research is under a CC BY-NC 4.0 International License Page 996 MATERIALS AND METHODS Study Area An assessment of halophytes flora was conducted along the GoK coast in 2011 to 2014 under Integrated Coastal Zone Management Project. The study area consisted of 4 districts (13 coastal talukas i.e. from Okha to Abdasa) surrounding the Gulf of Kachchh (22° 15’ N to 23° 50’ N and 68° 20’ E to 68° 54’ E) and its islands (Fig. 1). For the purpose of data collection the entire study area was categorized into four zones based on the district boundaries i.e. Devbhumi Dwarka, Jamnagar, Morbi and Kachchh. Fig 1: Study Area GoK Methodology For the present study random sampling method was followed. In the coastal areas, line transects of 500 m were laid perpendicular to HTL (High Tide Line) to landward side by using 5x5 Km grid maps of Land use/Land cover maps (Like forest, grasslands, scrublands etc.). Distance of 5 km. between two subsequent line intersects was maintained using Global Positioning System. Within each transect, quadrates were laid at the interval of 20 m for Trees and Shrubs 5m ×5m and for herbs, grasses, climbers 1m×1m [7-9]. To enrich the species inventory the opportunistic coastal area at each site (areas falling out side of the quadrates) were also explored and observed species were recorded and photographed. Collection of plant specimens was carried out to know more information on habitat and for preparation of herbarium specimens. The species were identified using published literature and different Floras [10-13]. Analysis of Bio-diversity: To measure α-biodiversity, it is necessary to measure specie richness, species diversity and the evenness of the species. Species richness is another good aspect for measuring biodiversity. Shannon Wiener diversity index: The Shannon diversity index sampling measure was utilised to randomly measure the individuals from an ‘indefinitely large’ (that is effectively infinite) population [14]. Species diversity was calculated using the equation [15]. H= -Ʃ pi ln pi Where, H’= Shannon index of general diversity, pi= the proportion abundance of the ith species= (ni/N), ni= The number of individuals in the ith species and N= The total number of individuals. Simpson’s index: The index of dominance of the community was calculated by Simpson’s index [16] as: c=Ʃni (ni (ni-1)/ N (N-1) Where c= Index of dominance, ni and N being the same as Shannon index of general diversity. Species richness index: Species richness S is the simplest measure of biodiversity and is simply a count of the number of different species in a given area. The index of species richness (d) was calculated by following [17] formula as- d = (S - 1) / ln N Where d = Margalef Diversity Index, S = Total number of species, N = Total number of individuals Evenness (equitability) index: The evenness (equitability) index of the community was calculated equation [18] as follows: E= H’/ In S Where H’= Shannon index and S- Number of species RESULTS AND DISCUSSION A total of species of 27 halophytes belonging to 23 genera and 14 families were encountered from GoK. Halophytes diversity includes 22 Dicot and 5 Monocot species. Among 13 talukas and Islands of GoK, the highest number (21) of halophyte species diversity was found in Islands of GoK and Bhachau taluka (20) followed by Mundra, Anjar and Khambaliya Talukas. The lowest numbers of halophyte species were observed in Lalpur Taluka (11) (Fig. 2 to Fig. 3).
  • 3. Int. J. Life. Sci. Scienti. Res., 3(3) MAY 2017 Copyright © 2015-2017| IJLSSR by Society for Scientific Research is under a CC BY-NC 4.0 International License Page 997 Fig 2: Taluka and Island wise Species richness of Halophytes in GoK Fig 3: Showing distribution pattern of Halophytes in the GoK (2011 - 2014) It is widely accepted that biodiversity of coastal flora is dependent on hydrological regime, geological and climatic conditions [19]. Although hydrology whether it is frequency of inundation or water source was the most important factor, remaining criteria such as, wetland morphology, vegetation type and geological locations were equally important for managing coastal ecosystem [20]. In the present study, Islands of GoK surrounded by sea water and having high saline habitat appear to support maximum halophytes diversity. However, the lowest diversity of halophytes was observed in Lalpur taluka, which has less saline area as compared to other talukas surrounding the GoK. The 36 species of halophytes were reported from India in the “book Monograph on Indian Halophytes” [13]. Present study reported 27 species of halophytes from GoK (Gujarat), among them two species viz. Haloxylon recurvum Bunge ex Boiss. and Zygophyllum simplex L., are not reported in the above said book [13]. Zygophyllum simplex L. was reported as halophyte in the book “Halophytes as a resource for livestock and for rehabilitation of degraded lands” [21]. H. recurvum Bunge ex Boiss. and Z. simplex was reported as Indian desert halophytes in the book “Contributions to the ecology of halophytes” [22]. Thus these two species were incorporated as halophytes in the present study.
  • 4. Int. J. Life. Sci. Scienti. Res., 3(3) MAY 2017 Copyright © 2015-2017| IJLSSR by Society for Scientific Research is under a CC BY-NC 4.0 International License Page 998 Similarity among the Talukas of GoK based on halophytes species distribution through Bray Curties similarity measure Considering the occurrence of the halophyte species and its composition, of Jamnagar, Jodiya, Kalyanpur, Maliya and Mandvi talukas were found to have highest similarity with each other i.e. 94%. Species composition of Okhamandal taluka showed 92% similarity of halophytes composition with Kalyanpur, Jamnagar and Jodiya taluka. The detailed similarity among the studied areas is given in Fig 4. Fig 4: Similarity among the Talukas of GoK based on halophytes species Halophytes Diversity in GoK Calculating biodiversity is a large part of determining the health of an ecosystem. The Shannon-Wiener Index (H’) and Simpson’s index (c) were used to determine which community is more diverse. The Simpson’s Index (c) employs data regarding the proportion of the species while the Shannon-Wiener Index (H’) includes information on species evenness and richness. These indices take quantitative numbers and express them into qualitative terms. Shannon-Wiener diversity index preferred over other diversity indices and its values vary between 0.0-5.0 [23]. Results between 1.5 to 3.5 are indicative of normal biological system and the index value exceeding 4.5 are rare. Values above 3.0 indicate that the structure of habitat is stable and balanced, while the values under 1.0 suggest that habitat structure is being seriously degraded by many factors such as climate change, anthropogenic pressure and pollution. From the present biodiversity study it was observed that the highest species diversity (Shannon-Wiener diversity) was observed in Jamnagar district and its islands (1.859) followed by Devbhumi Dwarka district and its islands (1.817), Morbi district (1.664) and Kachchh district (1.633) (Table 1). Thus the coastal areas of GoK has been revealing Shannon- Wiener diversity index in between 1.6 to 1.8, which indicate normal biological system and there is no degradation of habitat structure. The Simpson’s Index measures the probability that two individuals chosen at random will be the same species. Because of this, the range for the Simpson’s Index (c) is from Zero to One. Zero is the least diverse and one is the highest level of diversity attainable with this index [24]. From Simpson's index (c) it was observed that Jamnagar district and its islands (0.804) are highly diverse followed by Devbhumi Dwarka district and its islands (0.786), Morbi district (0.754) and Kachchh district (0.747) (Table 1). The study came with index of dominance of 0.252 for Kachchh district, 0.245 for Morbi district, 0.214 for Devbhumi Dwarka district and 0.196 for Jamnagar district (Table 1). It was reported that greater the value of index of dominance the lower the species diversity and vice versa in the scale of 0 to 1 [25]. Thus as highest index of dominance was observed in Kachchh district, the diversity is lowest in that region. Lowest index of dominance was observed in Jamnagar district and its islands thus the diversity was highest in that region. Since heterogeneity contains two separate ideas- species richness and evenness- it was only natural to try to measure the evenness component separately [26-27]. Evenness describes how equally individuals are distributed amongst the species. Pielou’s evenness index (e) was highest (0.528) in Morbi district followed by Jamnagar district and its islands (0.494), Devbhumi Dwarka district and its islands (0.0.647) and Kachchh district (0.365) (Table 1). Margalef species richness index (d) was highest in Devbhumi Dwarka district and its islands (1.519) followed by Kachchh district (1.373), Jamnagar district and its islands (1.262) and Morbi district (1.085) (Table 1).
  • 5. Int. J. Life. Sci. Scienti. Res., 3(3) MAY 2017 Copyright © 2015-2017| IJLSSR by Society for Scientific Research is under a CC BY-NC 4.0 International License Page 999 Table 2: Checklist of Halophytes Botanical Names / Sites 1 2 3 4 5 6 7 8 9 10 11 12 13 14 Aeluropus lagopoides (L.) Thwaites √ √ √ √ √ √ √ √ √ √ √ √ √ √ Arthrocnemum indicum (Willd.) Moq. √ × × × × × × × × × × × × × Artiplex stocksii(Wt.) Boiss. × √ × × × × × × × × × × × √ Cressa cretica L. √ √ √ √ √ √ √ √ √ √ √ √ √ √ Cyperus conglomeratus Rottb. √ √ √ √ √ √ √ √ × × √ √ √ √ Halopyrum mucronatum (L.) Stapf √ √ √ × √ √ √ × × √ √ √ √ √ Haloxylon recurvum Bunge ex Boiss. × × √ × √ √ √ × × √ √ √ √ √ Haloxylon salicornicum (Moq.) Bunge ex Boiss. √ √ √ √ √ √ √ × × √ √ √ √ √ Heliotropium curassavica L. × × √ × √ √ √ √ √ √ √ × √ √ Ipomoea pes-caprae (L.) R. Br. √ √ √ √ √ √ √ √ √ √ √ √ × √ Juncus maritimus Lam. × × × × × × √ √ × × × × √ √ Limonium stocksii Kuntze × × × × × × × √ × × × √ × √ Lotus garcini DC. √ × × × × × × √ × × × √ × × Prosopis juliflora (Sw.) DC. √ √ √ √ √ √ √ √ √ √ × √ √ √ Salicornia brachiata Miq. × × √ × √ √ √ √ × √ × × √ √ Salvadora persica L. √ √ √ √ √ √ √ √ √ √ √ √ √ √ Sericostoma pauciflorum Stocks ex. Wight √ √ √ √ × × × × × √ √ × × √ Sesuvium portulacastrum (L.) L. √ √ √ √ √ √ √ √ √ √ √ √ √ √ Sporobolus maderaspatanus Bor √ √ √ √ √ √ √ √ √ √ √ √ √ √ Suaeda fruticosa Forssk. ex. J.F.Gmel. √ √ √ √ √ √ √ √ √ √ √ √ √ √ Suaeda nudiflora Moq. √ √ √ √ √ √ √ √ √ √ √ √ √ √ Tamarix dioica Roxb. × √ √ √ √ × × × × √ √ √ √ √ Tamarix stricta Boiss. × × √ × × √ × √ × × × × × × Trianthema portulacastrum L. × √ × √ × × × × × × × √ × × Trianthema triquetra Rottler & Willd. × √ × × × × × √ × × × × × × Urochondra setulosa (Trin.) C.E.Hubb. √ √ √ √ √ √ √ √ √ √ √ √ √ √ Zygophyllum simplex L. × × √ × × × × × × × × × × × Total 16 18 20 15 17 17 17 18 11 17 17 18 17 21 Abadasa (1), Anjar (2), Bhachau (3), Gandhidham (4), Jamnagar(5), Jodiya(6), Kalyanpur (7), Khambhaliya (8), Lalpur (9), Maliya (10), Mandvi (11), Mundra (12), Okhamandal (13), Island (14), √=Present, ×= Absent Table 1: Various diversity indices of Halophytes in GoK Diversity indices Devbhumi Dwarka District and its islands Jamnagar District and its islands Morbi District Kachchh District Shannon-Wiener index (H') 1.817 1.859 1.664 1.633 Simpson's index (c ) 0.786 0.804 0.754 0.747 Dominance (1/c) 0.214 0.196 0.245 0.252 Evenness index (e) 0.410 0.494 0.528 0.365 Species richness (d) 1.519 1.262 1.085 1.373
  • 6. Int. J. Life. Sci. Scienti. Res., 3(3) MAY 2017 Copyright © 2015-2017| IJLSSR by Society for Scientific Research is under a CC BY-NC 4.0 International License Page 1000
  • 7. Int. J. Life. Sci. Scienti. Res., 3(3) MAY 2017 Copyright © 2015-2017| IJLSSR by Society for Scientific Research is under a CC BY-NC 4.0 International License Page 1001 Fig 5: Twenty-seven Halophyte plants species of Gulf of Kachchh (GoK) showed in Plate I and II Photographs
  • 8. Int. J. Life. Sci. Scienti. Res., 3(3) MAY 2017 Copyright © 2015-2017| IJLSSR by Society for Scientific Research is under a CC BY-NC 4.0 International License Page 1002 CONCLUSIONS The GoK is very rich in floral diversity. The present study reveals the presence of a total 27 species of halophytes. Diversity of halophyte plants community is highly valued now, since these ecosystems are being increasingly threatened by the current environmental crisis. The coastal area and islands of GoK have shown that the halophytes diversity is medium and indicate that the habitat structure showing normal biological system and there is no degradation of habitat structure. The present study will serve as a primary input towards monitoring and sustaining the phyto-diversity of halophytes in the coastal areas of GoK. Study on floristic distribution and diversity of halophytes will be useful to the conservation researchers, scientists and coastal zone managers for effective management of the coastal ecosystem of GoK. ACKNOWLEDGMENT The authors would like to thank GEER Foundation for giving the platform to carry out the research work. We would like to acknowledge other staff of the Foundation for field data collection and preparation of Maps. Thanks are also due to Department of Forests, Government of Gujarat and Marine National Park & Sanctuary for providing the permission to carry out this research. Authors are highly grateful to the World Bank, MoEF & CC, NPMU-SICOM, and SPMU-GEC for providing the financial assistance for this project under the Integrated Coastal Zone Management. REFERENCES [1] Nayak, S., Chauhan, P., Chauhan, H. B., Bahuguna, A. and Nath, N., IRS – 1C application for coastal zone management. Current science, 1996, 70 (7): 614-617. [2] Dijekema, K. S., Salt marshes in Europe. Nature and environment Series, 1984, No.30 pp. 178. [3] Beeftink, W. G., Salt marshes. In: The coastline. (Barnes, R. S. K. edt.) John Wiley and Sons, London 1977: 93-121. [4] Waisel, Y. and Ovadia, E., Biology of halophytes. Acad. Press, New York 1972: 184-193. [5] Hamdy, A. and Sardo, V., Halophytes: a precious resource. In: Hamdy, A. (ed.), El Gamal, F. (ed.), Lamaddalena, N. (ed.), Bogliotti, C. (ed.), Guelloubi, R. (ed.), Non-conventional water use: WASAMED project. Bari: CIHEAM / EU DG Research, 2005, No. 53: 119-128. [6] Lepping, O. and Daniels, F. J. A., Phytosociology of beach and salt marsh vegetation in northern west Greenland. Polarforschung, 2007, 76 (3):95-108. [7] Kershaw K.A., Quantitative and Dynamic plant ecology. 2nd Edn. Edward Arnold, London 1973; 308. [8] Misra, R., Ecology Work Book. Oxford and IBH publishing Co., Calcutta 1968, pp. 242. [9] Bonham, C. D., Measurements for terrestial Vegetatation. John Wiley & Sons, New York, N.Y. 1989; 338. [10]Shah, G. L., Flora of Gujarat State. Vol. I & II. Sardar Patel University Press, Vallabh Vidyanagar, 1978. [11]Cooke, T., The Flora of the Presidency of Bombay, Taylon & Francis, London, 1901-1908. [12]eHALOPH: http://www.sussex.ac.uk/affiliates/halophytes/ /index.php, The University of Sussex. [13]Joshi, A. J., Monograph on Indian Halophytes. Ocean & Atmospheric Science and Technology Cell. Dept. of Life Science, Bhavnagar University, India 2011:140. [14]Pielou, E.C., Ecological Diversity. Wiley, New York, 1975, pp. 165. [15]Margalef R., Perspectives in Ecological Theory. University of Chicago press, Chicago, IL 1968, pp. 111. [16]Simpson, E. H., Measurement of diversity. Nature, 1949, 163, pp.688. [17]Margalef, R., Temporal succession and spatial heterogeneity in phytoplankton. In: Perspectives in Marine biology, Buzzati-Traverso (ed.), Univ. Calif. Press, Berkeley 1958, pp. 323-347. [18]Pielou, E. C., The measurement of diversity in different types of biological collections. J. Theoret. Biol 1966, 13: 131-144. [19]Vyas. S. J. & Joshi, A. J., Study of diversity indices and ecological characteristic of coastal flora in ‘Bhal’ Region (Gujarat). IJPAES 2013, 3(2):261-267. [20]Green, D. L. Wetland Management Technical Manual. Environmental Studies Unit. Wetland classification, Department of Land and Water Conservation, NSW, 1997. [21]Victor R, Squires and Ayoub. A.T., Halophytes as a resource for livestock and for rehabilitation of degraded lands. Springer Science & Business Media. Kluwer Academic Publishers. 1994; 281-284. [22]Sen, David. N. and Rajpurohit, K. S., Contributions to the ecology of halophytes. Springer Science & Business Media. Dr. W. Junk Publishers. 1982, pp.70. [23]Turkmen and Kanachi., Applications of various biodiversity indices to benthic macro invertebrate assemblages in streams of a national park in Turkey. Review of Hydrobiology, Research article 2010, 3, 2:111-125. [24]Samantha R., "Biodiversity in a Florida Sandhill Ecosystem," Undergraduate Journal of Mathematical Modeling: One + Two 2009, 2(1), pp.1-14 [25]Misra K.C., Manual of Plant Ecology. 3rd Edition. NewDelhi: Oxford and IBH Publishing Co. Pvt. Ltd. 1989, pp. 491. [26]Lloyd, M. & Ghelardi, R.J., A table for calculating the "equitability" component of species diversity. J. Anim. Ecology 1964, 33: 217-225. [27]Krebs, C. J., Ecological methodology. Harper & Row, New Yourk 1989, pp. 471. International Journal of Life-Sciences Scientific Research (IJLSSR) Open Access Policy Authors/Contributors are responsible for originality, contents, correct references, and ethical issues. IJLSSR publishes all articles under Creative Commons Attribution- Non-Commercial 4.0 International License (CC BY-NC). https://creativecommons.org/licenses/by-nc/4.0/legalcode How to cite this article: Salvi H, Das L, Brahmbhatt B, Vaghela N, Kamboj RD: Diversity of Halophytes in Gulf of Kachchh, Gujarat. Int. J. Life. Sci. Scienti. Res., 2017; 3(3): 995-1002. DOI:10.21276/ijlssr.2017.3.3.6 Source of Financial Support: The World Bank, Conflict of interest: Nil