Journal of Threatened
Taxa | www.threatenedtaxa.org | 26 December 2024 | 16(12): 26240–26250
ISSN 0974-7907 (Online)
| ISSN 0974-7893 (Print)
https://doi.org/10.11609/jott.8366.16.12.26240-26250
#8366 | Received 12
January 2023 | Final received 30 November 2024 | Finally accepted 03 December
2024
A preliminary study
of odonate fauna in the high ranges of Munnar,
southern Western Ghats, India
T.S. Krishnanunni 1, Nazar
Neha 2, R. Arya 3 & P.O.
Nameer
1,2,3,4 College of Forestry,
Kerala Agricultural University, Thrissur, Kerala 680656, India.
1 tskrishnanunni@gmail.com,
2 neh.nazpkm@gmail.com, 3 aryaa.anilr@gmail.com, 4 nameer.po@kau.in
(corresponding author)
Editor: Ashish D. Tiple,
Dr. R.G. Bhoyar Arts, Commerce and Science College,
Wardha, India. Date of publication: 26 December
2024 (online & print)
Citation: Krishnanunni, T.S., Nazar
Neha, R. Arya & P.O. Nameer (2024). A preliminary study of odonate fauna in the high ranges of Munnar, southern
Western Ghats, India. Journal of Threatened Taxa 16(12):
26240–26250. https://doi.org/10.11609/jott.8366.16.12.26240-26250
Copyright: © Krishnanunni et al. 2024. Creative Commons
Attribution 4.0 International License. JoTT allows
unrestricted use, reproduction, and distribution of this article in any medium
by providing adequate credit to the author(s) and the source of publication.
Funding: We would like to express our profound appreciation to the Gol GEF UNDP IHRML Project for its logistical, financial, and technical assistance during the project.
Competing interests: The authors declare no competing interests.
Author details: Krishnanunni, T.S.—Erasmus Mundus scholar, currently pursuing master of science in European Forestry at the University of Natural Resources and Life Sciences (BOKU) Vienna, Austria. His research interest is broadened on remote sensing and GIS topics, spatial statistics, qualitative research and forest inventory and modelling, preparing for a career in research or academia. Neha Nazar—master’s student in Forest Ecology and Management at the University
of Alberta, Canada, supported by a Graduate Research Assistantship Fellowship. Her research focuses on understanding forest ecosystem dynamics, with a specific interest in coarse woody debris characteristics in post-fire and post-harvest remnants. Arya, R.-—completed her graduation from the College of Forestry, Kerala Agricultural University, Thrissur, Kerala and post-graduation in Forestry from College of Forestry, KSNUAHS, Shimoga, Karnataka. Nameer P.O.—professor
and head of the Department of Wildlife Sciences at Kerala Agricultural University, south India. His basic training is in forest ecology and ornithology. But works extensively on mammals, including bats. His current work includes biodiversity documentation of the Western Ghats, the study of the impact of climate change on the different taxa, citizen science, etc.
Author contributions: TSK—fieldwork, analysis and manuscript preparation. NN—fieldwork and analysis. AR—fieldwork and analysis. PON—principal supervisor throughout the project work and guidance during manuscript preparation.
Acknowledgements: We would like to
express our profound appreciation to the GoI GEF UNDP
IHRML Project for its logistical, financial, and technical assistance during the
project. We thank the then Munnar DFO, Mr. Raju Francis IFS and other officers
of the Munnar FD. We thank the dean,
College of Forestry, Kerala Agricultural University for the encouragement and
support. We wish to extend our gratitude to the professors in the Department of
Wildlife Science, KAU and Abin M. Sunil and Sreehari K. Mohan, the research scholars, for their
support.
Abstract: A study was
conducted at Munnar Forest Division Idukki District, Kerala, the southern
Western Ghats, to assess the diversity of odonates.
Around 44 species of odonates, which include 29
species of Anisoptera (dragonflies) and 15 species of
Zygoptera (damselflies). The odonate
diversity of Munnar Forest Division accounted for 24.72 % of the odonates in Kerala and 22.45 % of the odonates
of the Western Ghats. The study highlights the importance of biodiversity
documentation at high altitudes in the Western Ghats.
Keywords: Anisoptera,
biodiversity, ecosystem, endemic, Idukki District, Kerala, Odonata,
pre-monsoon, Zygoptera.
INTRODUCTION
The order Odonata is
one of the fascinating groups of winged insects which comprises both dragonflies
and damselflies (Grimaldi & Engel 2005). They act as an important top
predator at both larval and adult stages and hence form an important tool for
various types of assessments and monitoring, such as measures of biodiversity,
wetland health, integrity, and the biological impact of climate change. There
are over 6,376 odonate species known worldwide
(Paulson et al. 2022), 493 in India, 196 in the Western Ghats (Subramanian
& Babu 2020), and 178 in Kerala (Chandran et al.
2022; Society for Odonate Studies 2022). The 178
species of odonates of Kerala belong to 87 genera in two suborders and 14
families (Chandran et al. 2022; Society for Odonate
Studies 2022), and 68 species are endemic to the Western Ghats.
Studies on odonates of the Western Ghats are far and in between. These
include the studies by Mathavan & Miller (1989)
who reported 36 species of odonates from Periyar Tiger Reserve, Idukki District, Kerala; 29 species
of odonates were recorded from Silent Valley and New Amarambalam Reserved Forests in Kerala by Rao & Lahiri (1982), Emiliyamma & Radhakrishnan
(2000), recorded 25 species of odonates from Parambikulam Wildlife Sanctuary, Palakkad dt. Kerala, Adarsh et al. (2015) recorded 48 species of odonates from Chinnar Wildlife
Sanctuary, Idukki District, Kerala and Sadasivan et
al. (2022) recorded 116 species of odonates from Shendurney Wildlife Sanctuary, Kollam District, Kerala. The
present paper summarises the
findings of odonates from Munnar Forest
Division conducted during the pre-monsoon months: February to May 2022.
Study Area
The Munnar Forest
Division is located in the high ranges of the southern Western Ghats. It consists of
four ranges, namely Munnar Range, Devikulam Range, Adimaly Range, and Neriamangalam
Range with a total area of 892.707 km². The study focused on the hilly
regions (>1100 m) of the Munnar Forest Division, which majorly included the
Munnar and Devikulam Ranges. The study area is
located between 10.067–10.167 0N & 77.083–77.167 0E
(Figure 1). The details of the study localities are given in Table 1.
The topography of the
study area is hilly with undulating terrain. The altitude varies from 33 m near
Palamattom on the bank of the river Periyar
in the Neriamangalam Range to Anamudi
(2,695 m) in the Munnar Range. The average annual rainfall of the region is
about 3,000 mm, and it receives both southwestern and northeastern monsoons.
Temperatures range 6–35
°C, and the climate is more or less temperate in high-altitude
areas. The air is highly humid throughout the year, and the relative humidity
is about 80 % and above (Kerala Forest and Wildlife Department 2011).
The Munnar Forest
Division consists of different habitat types, which include, west coast
tropical evergreen forest, west coast semi-evergreen forest, southern moist
mixed deciduous forest, southern montane wet grasslands, the southern montane
wet temperate forest along with tea plantations, eucalyptus plantations,
cardamom hill reserves, and wattle plantations (Kerala Forest and
Wildlife Department 2011).
METHODS
The study was carried
out in the pre-monsoon months from February 2022 to May 2022 at selected
high-altitude sites (above 1,100 m) in the Munnar Forest Division. The field
was categorized into seven habitats, and three sites were randomly selected
from each habitat for surveying (21 sites in total). The habitats include
grassland, eucalyptus plantation, shola forest (southern montane wet temperate
forest), wattle plantations, pond and riverine ecosystem, Cardamom Hill Reserve
(evergreen), and tea plantation. A single field visit was made to each of the
three sites in each of the seven habitats between 0900 and 1300 h when odonate activity was at its peak. The belt transect
method (Kulkarni et al. 2013) was done to document odonates
and a 500 m transect line having a width of 10 m was taken on each site. The
transect and the coordinates were taken using a mobile application called ‘Geotracker’ (https://geo-tracker.org/).
Collection and
killing were avoided for species identification. Observed odonates
were photo-documented using a Nikon COOLPIX P900 and a Nikon D5600 DSLR camera
with a 70–300 mm lens. Most of the species were identified on the spot by close
observation and later confirmed using taxonomic monographs of Fraser (1933,
1934, 1936) and field guides (Subramanian 2009; Kiran & Raju 2013). The
taxonomy and nomenclature that have been used are as per Kalkman
et al. (2020). The odonates observed during the study
period were categorized into five groups based on their relative abundance.
Accordingly, those species which were sighted 80–100 % of the survey days were
categorized as very common (VC), 60–79 % as common (C), 40–59 % as occasional
(O), 20–39 % as rare (R), and very rare (VR) for those that were sighted less
than 20% of the field days. The species richness and abundance were recorded and Simpson & Shannon diversity indices and
evenness values were also calculated using PAST software.
RESULTS AND
DISCUSSION
The study has
encompassed 44 species of odonates, which include 29
species of Anisoptera (Dragonflies) and 15 species of
Zygoptera (Damselflies) spread across eight families
(Table 2). The family Libellulidae was the most
dominant in Anisoptera with 24 species, followed by Aeshnidae (3), Macromiidae (1),
and Gomphidae (1). Among Zygoptera,
Coenagrionidae (9) was the dominant family, followed
by Lestidae (3), Platycnemididae
(2), and Chlorocyphidae (1). Family-wise species
richness of odonates (both Anisoptera
and Zygoptera) along with their relative abundance is
given in Figure 2.
The distribution of odonates in the study area was classified into seven
different habitat types. Habitat-wise distribution and species diversity of odonates in the Munnar Forest Division are given in Table
3. Maximum species richness was observed in the pond and riverine ecosystem (26
species), followed by eucalyptus plantation (17 species), Cardamom Hill Reserve
(11 species), wattle infested areas (8), grassland (6 species), shola forest (6
species), and tea plantation (5). The species abundance was maximum in the pond
and riverine ecosystem and minimum in the shola forest.
The Simpson &
Shannon diversity indices and evenness values of the seven habitats were
calculated (Table 4). In this study, the value of the Gini Simpson’s index
ranged 0.794–0.932 in different habitats. The Simpson index showed the maximum
value for the pond and riverine ecosystem (0.932) and the minimum value for
grassland (0.794). Hence, species diversity is high in pond and riverine
ecosystem habitats. The value of the Shannon Weiner index for different
habitats range 1.47–2.87, with the maximum value shown by pond and riverine
ecosystem and the minimum by tea plantation. As a result, pond and riverine
ecosystems have the highest species richness and evenness.
Out of the 44 species
recorded, four of the odonate species are endemic,
two to the Western Ghats, one to peninsular India, and one to India. Esme cyaneovittata and Esme mudiensis
are endemic to the Western Ghats, Heliocypha
bisignata is endemic to peninsular India and Hylaeothemis apicalis is
endemic to India. There are 196 species of odonates
in the Western Ghats and 178 species of odonates in
Kerala. Considering the total number of species of Odonates
in Kerala, the present study accounted for 24.72 % of the odonates
in Kerala and 22.45 % of the odonates of the Western
Ghats. None of the odonate species from the region is
protected under the Indian Wildlife Protection Act (WPA) of 1972. According to
the IUCN Red List 2022, one species is staged under the ‘Not Evaluated’
category, four species under the ‘Data Deficient’ category, and the remaining
39 species are staged under the ‘Least Concern’ category, which implies that
none of the species from the present study is listed as a threatened species.
Due to their
amphibious life history, relatively short generation time, high trophic
position, and diversity, the order Odonata is considered an important component
of freshwater ecosystems as well as a good indicator of ecosystem health
(Corbet 1993). This reiterates the fact that more systematic exploration of
biodiversity should be carried out in unexplored regions of the Western Ghats,
especially in light of increasing anthropogenic influences and habitat
transformations. The present study highlights the existing diversity of
unexplored odonate fauna in the high ranges of the
Munnar Territorial Division. Major changes in the degradation quality of
available habitats could also result in a loss of regional odonate
diversity, especially for endemic species. These changes could also have a
cascading effect on terrestrial biodiversity.
A previous study on odonates from Chinnar Wildlife
Sanctuary (Adarsh et al. 2015), a component of Munnar Wildlife Division, has
recorded a total of 48 species of odonates, which
includes 31 species of dragonflies and 17 species of damselflies. The present
study has recorded 14 new records of odonates, which
include nine species
of dragonflies and five species of
damselflies.
The study also
highlights the sighting of Martin’s Duskhawker Anaciaeschna martini (Selys
1897) from wattle-infested areas of Idalimotta (above
2000m), which was previously recorded as a rediscovery from Nilgiris
in September 2014 and later from the Munnar region in the Anamalais
landscape of the Western Ghats in June 2019 (Sadasivan
et al. 2021). The observed individual was a female ovipositing
on emergent vegetation and no males were observed guarding or nearby the
female. The species was identified by the typical female morphological
characteristics of a brownish body with yellowish-green markings on the thorax
and a brownish-yellow abdomen, as well as a dark band along the leading edge of
the wings. Disturbed habitats such as wattle-infested areas may provide
suitable breeding sites and hunting grounds for species like Martin’s Duskhawker, which may explain the presence of this locally
‘not common’ species.
Even though there
have been frequent surveys and few published papers (Adarsh et al. 2015; Sadasivan et al. 2021) in the wildlife division of Munnar,
currently there are no published papers in Munnar territorial division as far
as odonates are concerned. Under the circumstance
that no previous research papers have been published under the Munnar
territorial division, the present study comes into the light, providing
far-reaching information regarding the diversity, distribution, and habitat
preference of the recorded odonate species during the
pre-monsoon period. The short-term study also acts as a preliminary report on odonates and forms a trail for further studies during the
monsoon and post-monsoon months, where a peak in species richness can be
expected due to the southwest monsoon.
Table 1. Details of
the study localities at Munnar Forest Division.
|
|
Habitat |
Coordinates |
Altitude (m) |
Weather |
Temperature (°C) |
Humidity (%) |
|
1 |
Grassland a) Chokramudi 1 b) Old Devikulam 2 c) Chokramudi 2 |
10.028 0N
& 77.102 0E 10.173 0N
& 77.179 0E 10.036 0N
& 77.123 0E |
1,736 1,788 1,736 |
Sunny Sunny Sunny |
25 23 25 |
48 47 48 |
|
2 |
Eucalyptus
plantation a) Devikulam b) KFRI Research
Station c) Signal Point |
10.067 0N
& 77.098 0E 10.072 0N
& 77.100 0E 10.071 0N
& 77.095 0E |
1,615 1,594 1,522 |
Cloudy Partly Cloudy Sunny |
24 22 24 |
68 63 47 |
|
3 |
Shola forest a) Aranmanai Shola b) Old Devikulam Shola c) Idalimotta Shola |
10.061 0N
& 77.140 0E 10.052 0N
& 77.163 0E 10.172 0N
& 77.183 0E |
1,676 1,801 2,239 |
Sunny Sunny Cloudy |
22 23 19 |
51 47 68 |
|
4 |
Wattle infested
area a) Idalimotta 1 b) Idalimotta 2 c) Idalimotta 3 |
10.173 0N
& 77.188 0E 10.171 0N
& 77.177 0E 10.171 0N
& 77.171 0E |
2,190 2,372 2,387 |
Cloudy Cloudy Cloudy |
17 17 17 |
95 95 95 |
|
5 |
Pond and riverine
ecosystem a) Erachilppara b) Seethadevi Lake c) Njandarmettu (CHR) |
10.066 0N
& 77.099 0E 10.045 0N
& 77.155 0E 9.965 0N
& 77.261 0E |
1,615 1,762 1,143 |
Partly cloudy Sunny Cloudy |
21 24 22 |
72 42 81 |
|
6 |
Cardamom Hill
Reserve a)Thalakkulam b)Njandarmettu c)Sankarapandyanmettu |
9.985 0N
& 77.220 0E 9.985 0N
& 77.221 0E 10.008 0N
& 77.199 0E |
1,254 1,143 1,249 |
Cloudy Cloudy Cloudy |
22 24 23 |
81 75 75 |
|
7 |
Tea plantation a) Signal Point
(KDHP) b) Lockhart (HNM
Tea estate) c) Madupatty Tea estate |
10.078 0N
& 77.091 0E 10.036 0N
& 77.122 0E 10.069 0N
& 77.096 0E |
1,537 1,518 1,630 |
Partly Cloudy Sunny Cloudy |
23 22 24 |
63 66 68 |
Table 2. Checklist of
odonates recorded from the study habitats of Munnar
Forest Division, Idukki, Kerala, southern Western Ghats.
|
|
Family/Scientific
name |
Endemicity |
IUCN status |
Abundance |
Study habitats |
|
A. |
Zygoptera (Damselflies) |
|
|||
|
|
Coenagrionidae |
|
|
|
|
|
1 |
Aciagrion approximans krishna Fraser, 1921 |
|
LC |
R |
P, C |
|
2 |
Aciagrion occidentale Laidlaw, 1919 |
|
LC |
O |
E, P, C |
|
3 |
Agriocnemis pieris Laidlaw, 1919 |
|
LC |
R |
E, W |
|
4 |
Agriocnemis pygmaea (Rambur, 1842) |
|
LC |
VR |
P |
|
5 |
Ceriagrion coromandelianum (Fabricius, 1798) |
|
LC |
VR |
P |
|
6 |
Ischnura rubilio Selys, 1876 |
|
NE |
VR |
P |
|
7 |
Ischnura senegalensis (Rambur, 1842) |
|
LC |
R |
G, P |
|
8 |
Pseudagrion microcephalum (Rambur, 1842) |
|
LC |
VR |
P |
|
9 |
Pseudagrion rubriceps Selys, 1876 |
|
LC |
VR |
P |
|
|
Platycnemididae |
|
|
|
|
|
10 |
Esme cyaneovittata Fraser, 1922 |
EN WG |
DD |
VR |
S |
|
11 |
Esme mudiensis Fraser, 1931 |
EN WG |
DD |
VR |
S |
|
|
Chlorocyphidae |
|
|
|
|
|
12 |
Heliocypha bisignata (Hagen in Selys,
1853) |
EN P |
LC |
VR |
S |
|
|
Lestidae |
|
|
|
|
|
13 |
Indolestes gracilis davenporti (Fraser, 1930) |
|
LC |
VC |
G, E, W, P, C, T |
|
14 |
Lestes dorothea Fraser, 1924 |
|
LC |
VR |
P |
|
15 |
Lestes elatus Hagen in Selys, 1862 |
|
LC |
VR |
P |
|
B. |
Anisoptera (Dragonflies) |
|
|||
|
|
Aeshnidae |
|
|
|
|
|
16 |
Anaciaeschna martini (Selys, 1897) |
|
LC |
VR |
P |
|
17 |
Anax immaculifrons Rambur, 1842 |
|
LC |
VR |
P |
|
18 |
Gynacantha dravida Lieftinck, 1960 |
|
DD |
VR |
E |
|
|
Libellulidae |
|
|
|
|
|
19 |
Acisoma panorpoides Rambur, 1842 |
|
LC |
R |
E, T |
|
20 |
Brachydiplax chalybea Brauer, 1868 |
|
LC |
VR |
P |
|
21 |
Brachydiplax sobrina (Rambur, 1842) |
|
LC |
O |
E, S, W, P |
|
22 |
Brachythemis contaminata (Fabricius,
1793) |
|
LC |
R |
E, P |
|
23 |
Bradinopyga geminata (Rambur, 1842) |
|
LC |
O |
G, E, T |
|
24 |
Crocothemis servilia (Drury, 1770) |
|
LC |
O |
G, E, W, C |
|
25 |
Diplacodes trivialis (Rambur, 1842) |
|
LC |
O |
E, W, T |
|
26 |
Hylaeothemis apicalis Fraser, 1924 |
EN I |
DD |
R |
P, C |
|
27 |
Orthetrum chrysis (Selys,
1892) |
|
LC |
O |
E, W, P, C |
|
28 |
Orthetrum glaucum (Brauer, 1865) |
|
LC |
VR |
C |
|
29 |
Orthetrum luzonicum (Brauer,1868) |
|
LC |
R |
G, C |
|
30 |
Orthetrum pruinosum (Burmeister, 1839) |
|
LC |
O |
E, P, T |
|
31 |
Orthetrum sabina (Drury, 1770) |
|
LC |
VR |
P |
|
32 |
Orthetrum triangulare (Selys,
1878) |
|
LC |
R |
W, C |
|
33 |
Palpopleura sexmaculata (Fabricius,
1787) |
|
LC |
VR |
E |
|
34 |
Pantala flavescens (Fabricius,
1798) |
|
LC |
R |
G, W |
|
35 |
Rhodothemis rufa (Rambur, 1842) |
|
LC |
VR |
P |
|
36 |
Sympetrum fonscolombii (Selys, 1840) |
|
LC |
VR |
S |
|
37 |
Tetrathemis platyptera Selys, 1878 |
|
LC |
O |
E, P, C |
|
38 |
Tramea limbata (Rambur, 1842) |
|
LC |
VR |
P |
|
39 |
Trithemis aurora (Burmeister, 1839) |
|
LC |
VR |
E |
|
40 |
Trithemis festiva (Rambur, 1842) |
|
LC |
VR |
E |
|
41 |
Urothemis signata (Rambur, 1842) |
|
LC |
VR |
P |
|
42 |
Zyxomma petiolatum Rambur, 184 |
|
LC |
R |
E, P |
|
|
Macromiidae |
|
|
|
|
|
43 |
Epophthalmia vittata Burmeister, 1839 |
|
LC |
VR |
C |
|
|
Gomphidae |
|
|
|
|
|
44 |
Ictinogomphus rapax (Rambur,1842) |
|
LC |
R |
S, P |
Legend: EN W—Endemic to Western Ghats | EN P—Endemic
to Peninsular India | EN I—Endemic to India.
LC—Least Concern |
DD—Data Deficient | NE—Not Evaluated.
G—Grassland |
E—Eucalyptus Plantation | S—Shola Forest | W—Wattle Plantation | P—Pond and
Riverine Ecosystem | C—Cardamom Hill Reserve | T—Tea Plantation.
Table 3. Habitat-wise
distribution of odonates at Munnar Forest Division.
|
Habitat |
Aeshnidae |
Chlorocyphidae |
Coenagrionidae |
Gomphidae |
Lestidae |
Libellulidae |
Macromiidae |
Platycnemididae |
|
Grassland |
0 |
0 |
2 |
0 |
7 |
8 |
0 |
0 |
|
Eucalyptus
Plantation |
1 |
0 |
6 |
0 |
7 |
23 |
0 |
0 |
|
Shola Forest |
0 |
2 |
0 |
1 |
0 |
2 |
0 |
3 |
|
Wattle Plantation |
0 |
0 |
2 |
0 |
5 |
9 |
0 |
0 |
|
Pond and Riverine
Ecosystem |
2 |
0 |
25 |
1 |
17 |
25 |
0 |
0 |
|
Cardamom Hill
Reserve |
0 |
0 |
7 |
0 |
4 |
15 |
1 |
0 |
|
Tea Plantation |
0 |
0 |
0 |
0 |
4 |
7 |
0 |
0 |
Table 4. Species
richness and diversity of odonates in high ranges of
Munnar Forest division.
|
Habitats |
Grassland |
Eucalyptus
plantation |
Shola forest |
Wattle plantation |
Pond and riverine
Ecosystem |
Cardamom Hill
Reserve |
Tea plantation |
|
Species richness |
6 |
17 |
6 |
8 |
26 |
11 |
5 |
|
Abundance |
17 |
37 |
8 |
16 |
70 |
27 |
11 |
|
Species relative
abundance |
0.14 |
0.39 |
0.14 |
0.18 |
0.59 |
0.25 |
0.11 |
|
Shannon's diversity
index (H') |
1.56 |
2.53 |
1.73 |
1.89 |
2.87 |
2.07 |
1.47 |
|
Simpson's diversity
index (D) |
0.21 |
0.08 |
0.07 |
0.12 |
0.07 |
0.131 |
0.182 |
|
Inverse Simpson's
diversity index (1/D) |
4.86 |
12.81 |
14.00 |
8.00 |
14.64 |
7.63 |
5.50 |
|
Gini Simpson's
index (1-D) |
0.79 |
0.92 |
0.93 |
0.88 |
0.93 |
0.87 |
0.82 |
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REFERENCES
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