Journal of Threatened
Taxa | www.threatenedtaxa.org | 26 May 2026 | 18(5): 28926–28939
ISSN 0974-7907 (Online) | ISSN 0974-7893 (Print)
https://doi.org/10.11609/jott.9696.18.5.28926-28939
#9696 | Received 19 February 2025 | Final received 26 February 2026|
Finally accepted 07 May 2026
A preliminary checklist of
dragonflies and damselflies (Insecta: Odonata) of
Kanyakumari District, Tamil Nadu, India
V. Muthukrishnan 1 , Anand Shibu 2 , Vinod Sadhasivan 3 &
R. Amirtha Balan 4
1,2 Kanyakumari District Forest
Office, Vadasery, Nagercoil,
Tamil Nadu 629001, India.
3 7/1d, Vini
Nivas ,
Moovendhar Nagar, Holy Cross College Road, Nagercoil, Tamil Nadu 629004, India.
4 Wildlife Institute of India, Chandrabani, Dehradun, Uttarakhand 248001, India.
1 avmkrish07@gmail.com
(corresponding author), 2 anandshibu12@gmail.com, 3 svinod@gmail.com,
4 amirthabalanrs13@gmail.com
Abstract: This study documents the Odonata
diversity in Kanyakumari District, Tamil Nadu, covering forested regions,
wetlands, reservoirs, and saltpans from September 2024 to January 2025. A total
of 82 species were recorded, including 47 dragonflies and 35 damselflies. The
highest diversity was observed at Mukkadal Dam,
followed by Mambazhathurayar Reservoir and Kannimaranthoppu stream. In contrast, Puthalam
Saltpan exhibited the lowest diversity likely due to high salinity levels.
Forested regions supported the greatest species richness, possibly due to their
relatively undisturbed, less polluted nature. This study contributes to the
documentation of regional biodiversity and supports the Biological Diversity
Act (2002) of India. The findings are expected to assist in local conservation
efforts and provide insights into Odonata habitat preferences in Kanyakumari
District.
Keywords: Anisoptera,
Balamore, Coenagrionidae,
endemic, Libellulidae, Puthalam
saltpan, Theroor wetland, Western Ghats, wetland, Zygoptera.
Editor: Anonymity requested. Date of publication: 26 May 2026 (online & print)
Citation: Muthukrishnan, V., A. Shibu, V. Sadhasivan
& R.A. Balan (2026). A preliminary checklist of dragonflies and
damselflies (Insecta: Odonata) of Kanyakumari
District, Tamil Nadu, India. Journal of
Threatened Taxa 18(5):
28926–28939. https://doi.org/10.11609/jott.9696.18.5.28926-28939
Copyright: © Muthukrishnan et al. 2026. 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: Zooreach Conservation Seed Grant 2024–25 (Project ID: 24ZCSG04I).
Competing interests: The authors declare no competing interests.
Author details: Muthukrishnan, V. is an independent researcher with a primary focus on biodiversity conservation and wildlife research. His work mainly emphasizes mammalian ecology, field-based biodiversity assessments, and conservation monitoring. He is skilled in conducting mammalian research using ecological survey techniques and contributes toward understanding and conserving wildlife populations and their habitats. Anand Shibu is a wildlife enthusiast with a strong passion for wildlife photography and biodiversity documentation. His interests focus on capturing and documenting wildlife diversity through visual narratives and field observations. He is also associated with local forest departments in supporting biodiversity documentation and wildlife-related conservation activities. Vinod Sadasivan is a dedicated wildlife enthusiast with a strong interest in biodiversity conservation, wildlife photography, and ecological documentation. His work focuses on biodiversity documentation and conducting wildlife awareness campaigns to promote conservation among the public. He is also associated with local forest departments in supporting wildlife monitoring and conservation-related activities. Amirtha Balan, R. is pursuing a Ph.D. at the Wildlife Institute of India, focusing on wildlife conservation. His research emphasizes herpetofaunal diversity, turtle ecology, biodiversity profiling, and ecological monitoring. He is particularly interested in understanding ecological patterns and contributing to science-based conservation strategies for threatened wildlife species and habitats.
Author contribution: Conceptualization & Study Design: Muthukrishnan, Vinod Sadasivan, Amirtha Balan; Data collection & analysis: Muthukrishnan, Anand Shibu, Amirtha Balan; Manuscript writing: Muthukrishnan, Amirtha Balan; Reviewed manuscript: Muthukrishnan, Anand Shibu, Vinod Sadasivan, Amirtha Balan R. All authors reviewed and approved the final manuscript.
Acknowledgments: We gratefully acknowledge the Zoo Outreach Organisation for funding support through the Zooreach Conservation Seed Grant 2024–25 (Project ID:
24ZCSG04I). We extend our sincere thanks to D. Jude for his guidance, A. Vidhya for field assistance, and all others who provided valuable support for this study.
Introduction
The order Odonata, encompassing
dragonflies and damselflies, is primarily associated with freshwater wetlands
and adjacent landscapes. It represents one of the most ancient insect lineages,
with fossil evidence indicating its origin dating back to the Permian period.
The term Odonata is derived from the Greek word odontos,
meaning “toothed”, referring to the characteristic dentition of their
mandibles. It comprises hemimetabolous insects with a
semi-aquatic life cycle (Corbet 1962; Stoks &
Córdoba-Aguilar 2012). They rely on freshwater ecosystems for reproduction,
with aquatic larval stages and terrestrial/aerial adult stages. Due to this
dependence, odonates serve as key bioindicators of
both aquatic and terrestrial habitats (Monteiro-Junior et al. 2014; Rocha-Ortega
et al. 2019). Although freshwater ecosystems cover only 0.8% of Earth’s surface
and account for merely 0.01% of the global water volume (Gatti
2016), they play a crucial role in sustaining biodiversity (Previsic
et al. 2014; Ivković & Plant 2015) and support
over 1,00,000 species (Gatti 2016).
Globally, the order Odonata
comprises 6,392 extant species distributed across 46 families (Paulson et al.
2026) and is found worldwide, except in polar regions. In India, the order is
represented by 506 species and 44 subspecies belonging to 157 genera, 17
families, and three suborders (Kalkman et al. 2020;
Subramanian & Babu 2024; Chandran et al. 2025).
Tamil Nadu comprises 147 species, of which 55 are endemic (Subramanian & Babu 2024).
Odonates, being habitat specialists, are
primarily associated with primary forests, open plains, and tropical streams
(Villanueva & Mohagan 2010; Koparde
et al. 2014, 2015). Notably, dragonflies and damselflies exhibit differential
responses to habitat modifications, with damselflies being more sensitive to
microhabitat changes (Koparde 2016). Due to their
ecological roles, odonates are regarded as key
components of aquatic ecosystems and serve as biological indicators of
environmental conditions (Clark & Samways 1996; Samways et al. 1989).
Subramanian (2007) reported 178 species of odonates
from the Western Ghats with 68 endemic species. Emiliyamma
(2014) reported 169 species of odonates from southern
Western Ghats with 66 endemic species.
Kanyakumari District, formerly
part of the Travancore State before India’s independence, was historically
known as South Travancore District (Menon & Padmanabha
1929) and later integrated into Tamil Nadu. While historical faunal records
from Travancore exist, many lack precise locality data. This study represents
one of the first dedicated surveys on Odonata diversity in Kanyakumari District
in nearly a century, contributing valuable insights into the region’s unique
Odonata assemblages.
Given the significance of
regional biodiversity documentation for long-term conservation and management,
a systematic study was conducted across varied habitats of Kanyakumari
District, Tamil Nadu, southern India, from September 2024 to January 2025. The
findings of this research are presented herein.
Study area
The present study was conducted
across multiple sites in Kanyakumari District, encompassing both forested
regions (natural plantation with rich canopy) (Kannimaranthoppu
scrub forest elevation ranges 100–140 m, Mahendragiri
Reserve Forest; Balamore Estate elevation ranges
400–480 m, with fragmented moist evergreen forest; Kothayar
elevation ranges 200–250 m, with moist deciduous forest), Freshwater wetlands (Mambazhathurayar Reservoir located in Villukuri,
with dry deciduous forest elevation 99 m; Mukkadal
Dam built across the Vambaru River, with dry
deciduous forest elevation 57 m; Thovalai Checkdam built across Thovalai
Canal, elevation 53 m; Putheri lake receives water
from a canal outlet of Pechiparai Dam, elevation 17
m; Periyakulam near the town of Manavalakurichi,
elevation 10 m; Theroor wetland receives water from Thovalai Channel, elevation 32 m; Thirunanthikarai
receives water source from Nandhiaaru River (Kodayar left bank canal), elevation 92 m, and Puthalam Saltpan receives water from the Manakkudy Estuary, elevation 8 m). Forests cover
approximately 30% of the district, extending over 40,000 ha, situated between
8.076°–8.578° N and 77.100°–77.590° E. This survey aimed to assess Odonata
richness across diverse habitat types, including forest streams (Kannimaranthoppu—KMT, Balamore
Estate—BE, & Kothayar—KTF), reservoirs (Mambazhathurayar—MTY & Mukkadal
dam—MD), selected wetlands (Thovalai Checkdam—TCD, Putheri lake—PL, Periyakulam—PK, Theroor
wetland—TW, & Thirunanthikarai–TNK), and saltpans
(Puthalam Saltpan–PSP) (Table 1; Figure 1; Image 1).
The study was conducted from September 2024 to January 2025.
Materials
and Methods
The Odonata survey was conducted
primarily during daylight hours using the line transect & visual encounter
survey method, everyday from 0600 to 1000 h, from
September 2024 to January 2025. The study relied predominantly on photographic
documentation rather than specimen collection, due to the Tamil Nadu Forest
Department’s stringent regulations on faunal collection. This policy contrasts
with those of the neighbouring states, Kerala and
Karnataka, and has contributed to the scarcity of faunal records from this
region of the Western Ghats.
Digital photographs were captured
using a Nikon D7000 camera equipped with a 300 mm lens. Species identification
was performed using available reference literature, including Subramanian
(2009) and Kiran & Raju (2013).
Results
During the study period, a total
of 82 Odonata species were recorded, comprising 47 dragonfly (Anisoptera) and 35 damselfly (Zygoptera)
species (Table 2, Images 2–6) belonging to 13 families and 57 genera. Of the 82
species, 18 species are endemic. Species richness varied across the surveyed
locations. The highest number of species was observed at Mukkadal
Dam, where 37 dragonfly species and 17 damselfly species were recorded,
followed by Mambazhathurayar Reservoir with 31
dragonfly species and 13 damselfly species. The Kannimaranthoppu
Stream habitat also exhibited a high number of species, with 29 dragonfly species
and 15 damselfly species.
In contrast, Puthalam
Saltpan, a high-salinity habitat, exhibited the lowest number of species, with
15 dragonfly species and six damselfly species, as elevated salinity levels are
generally unsuitable for most Odonata species, except for a few
salinity-tolerant species. Further study is required to understand the species
habitat preference.
Other surveyed locations recorded
moderate species richness: Kothayar Twin Falls (38
species), Periyakulam (37 species), Thirunanthikarai (35 species), Theroor
Wetland (33 species), Putheri Lake (31 species), Balamore Estate (30 species), and Thovalai
checkdam (25 species). Survey efforts at Balamore
Estate were limited to three replicates, as the region falls largely within a
protected area where research activities were restricted due to lack of
permission and other constraints (Figure 2).
The documented species are
classified under various IUCN Red List categories, with the ‘Least Concern’
(LC) category comprising 42 species of dragonflies (Anisoptera)
and 27 species of damselflies (Zygoptera).
Additionally, one dragonfly Heliogomphus promelas is categorized as ‘Near Threatened’ (NT),
while one damselfly Protosticta sanguinostigma falls under the ‘Vulnerable’ (VU)
category. Furthermore, eight species (Gynacantha
dravida, Macrogomphus
wynaadicus,
Hylaeothemis apicalis
and Idionyx travancorensis
dragonflies and Caconeura ramburi, Caconeura risi, Esme mudiensis
and Protosticta rufostigma
damselflies) are classified as ‘Data Deficient’ (DD), while two damselflies Vestalis submontana
and Indolestes gracilis
davenporti and one dragonfly Merogomphus
tamaracherriensis remain ‘Not Evaluated’ (NE)
(Table 2). Platycnemididae and Gomphidae
have the highest number of DD and NE species, respectively, on the IUCN Red
List.
Libellulidae is the most species-rich family,
comprising 35 species, followed by Coenagrionoidea
with 14 species, and Platycnemididae with seven
species, which are considered moderate in terms of species-rich families.
Several families, including Macromiidae, Platystictidae, Protostictidae,
and Synthemistidae, are represented by one species
each. The distribution of species richness among these families reflects
differential patterns of abundance and taxonomic representation within the
Odonata order across Kanyakumari District (Figure 3).
Discussion
The study on Odonata in
Kanyakumari District recorded 82 species, representing about 55.78% of Tamil
Nadu’s total (147 species). It notably documented 18 endemic species, making up
32.73% of the state’s known endemics (Subramanian & Babu
2024). The findings, with 47 dragonflies and 35 damselflies, surpass other
regional surveys, such as the Madurai District (28 species), the Mettur Dam region in Salem (40 species), Coimbatore (69
species), and the Vellore District (30–37 species) (Muhil
& Pramod 2017; Ganeswari & Rajendran 2025)
establishing Kanyakumari as a biodiversity hotspot. This richness is attributed
to its proximity to the Western Ghats, a global biodiversity hotspot with 176
Odonata species, 68 of which are endemic (Subramanian 2008; Subramanian et al.
2009).
The variation in species richness
across the study sites highlights the importance of habitat heterogeneity. High
diversity at Mukkadal Dam and Kannimaranthoppu
Stream aligns with previous studies showing that forest streams and permanent
water bodies support high Odonata species richness (Muhil
& Pramod 2017). These environments offer stable conditions and complex
microhabitats crucial for larval development and adult territoriality
(Subramanian 2005; Vignesh & Manivannan 2021). In
contrast, the low species count at Puthalam Saltpan
indicates Odonata’s sensitivity to high salinity,
reinforcing their role as bioindicators of environmental health and water
quality (Kunte 2000; Tiple
2020).
Taxonomically the Libellulidae family, with 35 species, dominates Odonata
assemblages in Tamil Nadu and India (Koli et al.
2015; Tiple 2020; Ganeswari
& Rajendran 2025) attributed to their shorter life cycles, adopt to a wide
range of habitat (Gentry et al. 1975; Samways 1989), high dispersal capacity,
and habitat adaptability (Ganeswari & Rajendran
2025). Similarly, Coenagrionidae, the second most
speciose group with 14 species, also shows a similar prevalence, reflecting
their tolerance for diverse wetland types and preference for areas with
emergent vegetation.
The odonates
documented from Kanyakumari District conservation profile features several
species with specialized requirements. Most are classified as LC, but the VU
damselfly Protosticta sanguinostigma
and NT dragonfly Heliogomphus promelas highlight the region’s ecological importance (Muhil & Pramod 2017). Protosticta
sanguinostigma thrives in specialized forest
habitats, which face threats from fragmentation and land-use changes (Paray & Mir 2023; Samanta et
al. 2023). Additionally, many species are categorized as DD or NE, reflecting a
wider issue in Indian odonatology regarding limited
taxonomic and distributional data. Members of the Gomphidae
family are fast-moving insects, with some being crepuscular and many considered
rare, making them difficult to detect during surveys (Tiple
& Koparde 2015).
The study examined various
aquatic habitats in the district but did not include forest areas, particularly
within the Kanyakumari Wildlife Sanctuary. Challenges at Balamore
Estate, due to its protected status, hindered a comprehensive biodiversity
census. The findings highlight the need for strict protection of Kanyakumari’s
freshwater resources, as urbanization (Sánchez-Bayo
& Wyckhuys 2019), pollution (Tiple
et al. 2013; Tiple & Koparde
2015), and wetland loss threaten Odonata species, emphasizing the importance of
conserving both common and endangered taxa.
Table 1. List of study
site across Kanyakumari District.
|
|
Study site |
Elevation (m) |
Location |
|
1 |
Kannimaranthoppu, Mahendragiri Reserve Forest |
100–140 |
08.348° N, 77.514° E |
|
2 |
Balamore Estate |
400–480 |
08.458° N, 77.392° E |
|
3 |
Kothayar Twin Falls |
200–250 |
08.491° N, 77.327° E |
|
4 |
Mambazhathurayar Reservoir, Villukuri |
99 |
08.233° N, 77.378° E |
|
5 |
Mukkadal Dam |
57 |
08.280° N, 77.409° E |
|
6 |
Thovalai Checkdam |
53 |
08.235° N, 77.505° E |
|
7 |
Putheri Lake |
17 |
08.205° N, 77.426° E |
|
8 |
Periyakulam, Manavalakurichi |
10 |
08.170° N, 77.306° E |
|
9 |
Theroor Wetland, Thovalai Channel |
32 |
08.178° N, 77.461° E |
|
10 |
Thirunanthikarai |
92 |
08.397° N, 77.296° E |
|
11 |
Puthalam Saltpan |
8 |
08.112° N, 77.471° E |
Table 2. A checklist of dragonflies
and damselflies of Kanyakumari District, Tamil Nadu.
IUCN—International Union for Conservation
of Nature | LC-—Least Concern | DD—Data Deficient | NT—Near Threatened | VU—Vulnerable | NE—Not Evaluated | BE—Balamore Estate | KMT—Kannimaranthoppu |
KTF—Kothayar Twin
Falls | MTY—Mambazhathurayar
Reservoir | MD—Mukkadal Dam | PK—Periyakulam | PS—Puthalam Saltpan | PL— utheri Lake | TW—Theroor Wetland | TNK—Thirunanthikarai | TCD—Thovalai Check Dam | “✔”— Presence | “—”—Absence. * Endemic Taxa.
|
|
Scientific name |
Common name |
IUCN Red List status |
BE |
KMT |
KTF |
MTY |
MD |
PK |
PS |
PL |
TW |
TNK |
TCD |
|
|
Suborder Anisoptera
Selys, 1854 |
|||||||||||||
|
|
Family: Aeshnidae
Leach, 1815 |
|||||||||||||
|
1 |
Anax guttatus (Burmeister, 1839) |
Lesser Green Emperor |
LC |
- |
— |
— |
— |
— |
✔ |
✔ |
✔ |
✔ |
— |
— |
|
2 |
Anax immaculifrons Rambur, 1842 |
Magnificient Emperor |
LC |
✔ |
— |
✔ |
— |
✔ |
— |
— |
— |
— |
— |
✔ |
|
3 |
Anax indicus Lieftinck, 1942 |
Elephant Emperor |
LC |
— |
✔ |
— |
✔ |
✔ |
✔ |
✔ |
— |
✔ |
— |
— |
|
4 |
Gynacantha dravida Lieftinck, 1960 |
Indian Duskhawker |
DD |
— |
— |
— |
✔ |
✔ |
— |
— |
— |
— |
✔ |
— |
|
|
Family: Gomphidae
Rambur, 1842 |
|||||||||||||
|
5 |
Heliogomphus promelas (Selys, 1873)* |
Indian Lyrtail |
NT |
— |
— |
✔ |
— |
— |
— |
— |
— |
— |
— |
— |
|
6 |
Ictinogomphus rapax (Rambur, 1842) |
Indian Common Clubtail |
LC |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
— |
— |
✔ |
✔ |
— |
|
7 |
Macrogomphus wynaadicus Fraser, 1924* |
Wyanad Bowtail |
DD |
✔ |
— |
— |
— |
— |
— |
— |
— |
— |
— |
— |
|
8 |
Merogomphus tamaracherriensis Fraser, 1931* |
Malabar Long-legged Clubtail |
NE |
— |
— |
✔ |
— |
— |
— |
— |
— |
— |
— |
— |
|
9 |
Microgomphus souteri Fraser, 1924* |
Pygmy Clubtail |
LC |
— |
— |
✔ |
— |
✔ |
— |
— |
— |
— |
— |
— |
|
10 |
Paragomphus lineatus (Selys, 1850) |
Lined Hooktail |
LC |
— |
✔ |
✔ |
✔ |
✔ |
— |
— |
— |
— |
— |
— |
|
|
Family: Libellulidae
Leach, 1815 |
|||||||||||||
|
11 |
Acisoma panorpoides Rambur, 1842 |
Trumpet-Tail |
LC |
— |
✔ |
— |
✔ |
✔ |
✔ |
— |
✔ |
✔ |
— |
✔ |
|
12 |
Aethriamanta brevipennis (Rambur, 1842) |
Scarlet Marsh Hawk |
LC |
— |
— |
— |
✔ |
— |
✔ |
— |
✔ |
— |
— |
✔ |
|
13 |
Brachydiplax chalybea Brauer, 1868 |
Rufous-backed Marsh Hawk |
LC |
— |
✔ |
— |
✔ |
✔ |
✔ |
— |
✔ |
— |
— |
— |
|
14 |
Brachydiplax sobrina (Rambur, 1842) |
Little Blue Marsh Hawk |
LC |
— |
— |
— |
✔ |
✔ |
✔ |
— |
✔ |
✔ |
— |
✔ |
|
15 |
Brachythemis contaminata (Fabricius, 1793) |
Ditch Jewel |
LC |
— |
✔ |
— |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
|
16 |
Bradinopyga geminata (Rambur, 1842) |
Granite Ghost |
LC |
✔ |
✔ |
✔ |
✔ |
— |
— |
— |
— |
— |
— |
✔ |
|
17 |
Cratilla lineata (Brauer, 1878) |
Emerald-Banded Skimmer |
LC |
✔ |
— |
✔ |
— |
— |
— |
— |
— |
— |
— |
— |
|
18 |
Crocothemis servilia (Drury, 1770) |
Scarlet Skimmer |
LC |
— |
✔ |
— |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
— |
— |
|
19 |
Diplacodes trivialis (Rambur, 1842) |
Blue Ground Skimmer |
LC |
— |
— |
— |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
— |
— |
|
20 |
Hydrobasileus croceus (Brauer, 1867) |
Amber-winged Marsh Glider |
LC |
— |
✔ |
✔ |
✔ |
✔ |
✔ |
— |
✔ |
✔ |
— |
— |
|
21 |
Hylaeothemis apicalis Fraser, 1926* |
Blue Hawklet |
DD |
✔ |
— |
✔ |
— |
— |
— |
— |
— |
— |
— |
— |
|
22 |
Indothemis carnatica (Fabricius, 1798) |
Light-tipped Demon |
LC |
— |
✔ |
— |
— |
— |
— |
— |
— |
— |
— |
— |
|
23 |
Lathrecista asiatica (Fabricius, 1798) |
Asiatic Blood-Tail |
LC |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
|
24 |
Macrodiplax cora (Brauer, 1867) |
Estuarine Skimmer |
LC |
— |
— |
— |
— |
✔ |
✔ |
✔ |
✔ |
✔ |
— |
— |
|
25 |
Neurothemis tullia (Drury, 1773) |
Pied Paddy Skimmer |
LC |
— |
✔ |
— |
✔ |
✔ |
✔ |
— |
✔ |
✔ |
✔ |
— |
|
26 |
Onychothemis testacea Laidlaw, 1902 |
River Hawker |
LC |
— |
— |
✔ |
— |
✔ |
— |
— |
— |
— |
✔ |
— |
|
27 |
Orthetrum chrysis (Selys, 1891) |
Brown-Backed Marsh Hawk |
LC |
— |
✔ |
✔ |
— |
✔ |
— |
— |
— |
— |
✔ |
✔ |
|
28 |
Orthetrum glaucum (Brauer, 1865) |
Blue Marsh Hawk |
LC |
✔ |
✔ |
✔ |
✔ |
✔ |
— |
— |
— |
— |
✔ |
— |
|
29 |
Orthetrum luzonicum (Brauer, 1868) |
Tri-coloured
Marsh Hawk |
LC |
— |
✔ |
✔ |
✔ |
✔ |
✔ |
— |
— |
— |
✔ |
✔ |
|
30 |
Orthetrum pruinosum (Burmeister, 1839) |
Crimson-tailed Marsh |
LC |
— |
✔ |
✔ |
✔ |
✔ |
— |
— |
— |
— |
✔ |
✔ |
|
31 |
Orthetrum sabina (Drury, 1770) |
Green Marsh Hawk |
LC |
— |
✔ |
— |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
|
32 |
Pantala flavescens (Fabricius, 1798) |
Wandering Glider |
LC |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
|
33 |
Potamarcha congener (Rambur, 1842) |
Yellow-tailed Ashy Skimmer |
LC |
— |
✔ |
✔ |
✔ |
✔ |
✔ |
— |
— |
✔ |
— |
✔ |
|
34 |
Rhodothemis rufa (Rambur, 1842) |
Rufous Marsh Glider |
LC |
— |
— |
— |
✔ |
✔ |
✔ |
— |
✔ |
✔ |
— |
— |
|
35 |
Rhyothemis variegata (Linnaeus, 1763) |
Common Picturewing |
LC |
— |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
|
36 |
Tetrathemis platyptera Selys, 1878 |
Pygmy Skimmer |
LC |
— |
— |
✔ |
— |
— |
— |
— |
— |
— |
— |
— |
|
37 |
Tholymis tillarga (Fabricius, 1798) |
Coral-tailed Cloudwing |
LC |
— |
✔ |
— |
✔ |
✔ |
✔ |
— |
✔ |
✔ |
✔ |
— |
|
38 |
Tramea basilaris (Palisot de Beauvois, 1805) |
Red Marsh Trotter |
LC |
✔ |
✔ |
— |
— |
✔ |
✔ |
✔ |
✔ |
✔ |
— |
✔ |
|
39 |
Tramea limbata (Desjardins, 1832) |
Black Marsh Trotter |
LC |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
|
40 |
Trithemis aurora (Burmeister, 1839) |
Crimson Marsh Glider |
LC |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
|
41 |
Trithemis festiva (Rambur, 1842) |
Black Stream Glider |
LC |
✔ |
✔ |
✔ |
✔ |
✔ |
— |
— |
— |
— |
✔ |
✔ |
|
42 |
Trithemis pallidinervis (Kirby, 1889) |
Long-legged Marsh Glider |
LC |
— |
✔ |
— |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
— |
✔ |
|
43 |
Urothemis signata (Rambur, 1842) |
Greater Crimson Glider |
LC |
✔ |
✔ |
— |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
— |
✔ |
|
44 |
Zygonyx iris Selys, 1869 |
Emerald Cascader |
LC |
✔ |
✔ |
✔ |
— |
✔ |
— |
— |
— |
— |
✔ |
— |
|
45 |
Zyxomma petiolatum Rambur, 1842 |
Long-tailed Dusk Darter |
LC |
— |
— |
— |
✔ |
✔ |
✔ |
— |
✔ |
✔ |
— |
— |
|
|
Family: Macromiidae
Needham, 1903 |
|||||||||||||
|
46 |
Epophthalmia vittata Burmeister, 1839 |
Common Torrent Hawk |
LC |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
— |
— |
✔ |
✔ |
— |
|
|
Family: Synthemistidae
Tillyard, 1911 |
|||||||||||||
|
47 |
Idionyx travancorensis Fraser, 1931 |
- |
DD |
✔ |
— |
— |
— |
— |
— |
— |
— |
— |
— |
— |
|
|
Zygoptera Selys, 1854 |
|||||||||||||
|
|
Family: Chlorocyphidae
Cowley, 1937 |
|||||||||||||
|
48 |
Heliocypha bisignata (Hagen in Selys, 1853)* |
Stream Ruby |
LC |
✔ |
✔ |
✔ |
✔ |
✔ |
— |
— |
— |
— |
✔ |
— |
|
49 |
Libellago indica (Fraser, 1928)* |
Southern Heliodor |
LC |
— |
— |
— |
✔ |
✔ |
— |
— |
— |
— |
✔ |
— |
|
|
Family: Calopterygidae
Selys, 1850 |
|||||||||||||
|
50 |
Neurobasis chinensis (Linnaeus, 1758) |
Stream Glory |
LC |
✔ |
✔ |
✔ |
— |
— |
— |
— |
— |
— |
✔ |
— |
|
51 |
Vestalis apicalis Selys, 1873 |
Black-tipped Forest Glory |
LC |
✔ |
✔ |
✔ |
✔ |
✔ |
— |
— |
— |
— |
✔ |
— |
|
52 |
Vestalis gracilis (Rambur, 1842) |
Clear-winged Forest Glory |
LC |
✔ |
✔ |
✔ |
✔ |
✔ |
— |
— |
— |
— |
✔ |
— |
|
53 |
Vestalis submontana Fraser, 1934* |
Montane Forest Glory |
NE |
— |
— |
✔ |
— |
— |
— |
— |
— |
— |
— |
— |
|
|
Family: Coenagrionidae
Kirby, 1890 |
|||||||||||||
|
54 |
Aciagrion approximans (Selys, 1876) |
Indian Violet Dartlet |
LC |
✔ |
— |
— |
— |
— |
— |
— |
— |
— |
— |
— |
|
55 |
Agriocnemis pygmaea (Rambur, 1842) |
Pygmy Dartlet |
LC |
— |
— |
— |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
|
56 |
Agriocnemis splendidissima Laidlaw, 1919 |
Splendid Dartlet |
LC |
— |
— |
— |
— |
✔ |
— |
— |
— |
— |
— |
— |
|
57 |
Ceriagrion cerinorubellum (Brauer,
1865) |
Orange-tailed Marsh Dart |
LC |
— |
— |
— |
— |
— |
✔ |
— |
— |
— |
— |
— |
|
58 |
Ceriagrion coromandelianum (Fabricius,
1798) |
Coromandel Marsh Dart |
LC |
— |
✔ |
— |
✔ |
✔ |
✔ |
— |
✔ |
✔ |
✔ |
✔ |
|
59 |
Ischnura rubilio Selys, 1876 |
Western Golden Dartlet |
LC |
— |
✔ |
— |
— |
— |
— |
✔ |
✔ |
— |
— |
— |
|
60 |
Ischnura senegalensis (Rambur, 1842) |
Senegal Golden Dartlet |
LC |
— |
✔ |
— |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
— |
✔ |
|
61 |
Paracercion malayanum (Selys, 1876) |
Malayan Lily-Squatter |
LC |
— |
— |
— |
— |
— |
✔ |
✔ |
✔ |
✔ |
— |
— |
|
62 |
Pseudagrion decorum (Rambur, 1842) |
Three-lined Sprite |
LC |
— |
✔ |
— |
— |
— |
✔ |
— |
— |
— |
— |
— |
|
63 |
Pseudagrion indicum Fraser, 1924* |
Yellow-striped Sprite |
LC |
— |
— |
— |
— |
✔ |
— |
— |
— |
— |
— |
— |
|
64 |
Pseudagrion microcephalum (Rambur, 1842) |
Blue Sprite |
LC |
— |
✔ |
— |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
✔ |
— |
|
65 |
Pseudagrion rubriceps Selys, 1876 |
Saffron-faced Blue Sprite |
LC |
— |
✔ |
— |
✔ |
✔ |
✔ |
— |
✔ |
✔ |
✔ |
✔ |
|
|
Family: Euphaeidae
Yakobson & Bainchi,
1905 |
|||||||||||||
|
66 |
Dysphaea ethela Fraser, 1924* |
Black Torrent Dart |
LC |
✔ |
— |
✔ |
— |
✔ |
— |
— |
— |
— |
— |
— |
|
67 |
Euphaea fraseri (Laidlaw, 1920*) |
Malabar Torrent Dart |
LC |
✔ |
✔ |
✔ |
✔ |
✔ |
— |
— |
— |
— |
✔ |
— |
|
|
Family: Lestidae
Calvert, 1907 |
|||||||||||||
|
68 |
Indolestes gracilis davenporti Fraser, 1930* |
Davenport's False Spreadwing |
NE |
✔ |
— |
— |
— |
— |
— |
— |
— |
— |
— |
— |
|
69 |
Lestes concinnus Hagen in Selys, 1862 |
Dusky Spreadwing |
LC |
— |
✔ |
— |
— |
— |
— |
— |
— |
— |
— |
— |
|
70 |
Lestes elatus Hagen in Selys, 1862 |
Emerald Spreadwing |
LC |
— |
— |
— |
— |
✔ |
— |
✔ |
— |
✔ |
— |
✔ |
|
71 |
Lestes praemorsus Hagen in Selys, 1862 |
Scalloped Spreadwing |
LC |
— |
— |
— |
✔ |
✔ |
— |
— |
— |
— |
— |
— |
|
|
Family: Coenagrionoidea
Kirby, 1890 |
|||||||||||||
|
72 |
Agriocnemis pieris Laidlaw, 1919 |
Indian White Dartlet |
LC |
— |
— |
— |
— |
— |
— |
— |
— |
— |
✔ |
— |
|
|
Family: Platycnemididae
Yakobson & Bainchi,
1907 |
|||||||||||||
|
73 |
Copera marginipes (Rambur, 1842) |
Yellow Bush Dart |
LC |
— |
✔ |
✔ |
✔ |
✔ |
✔ |
— |
✔ |
✔ |
✔ |
— |
|
74 |
Caconeura ramburi (Fraser, 1922)* |
Indian Blue Bambootail |
DD |
— |
✔ |
— |
— |
— |
— |
— |
— |
— |
— |
— |
|
75 |
Caconeura risi (Fraser, 1922)* |
Wayanad Bambootail |
DD |
✔ |
— |
✔ |
— |
— |
— |
— |
— |
— |
✔ |
— |
|
76 |
Copera vittata Selys, 1863 |
Blue Bush Dart |
LC |
— |
— |
— |
— |
— |
— |
— |
— |
— |
✔ |
— |
|
77 |
Esme mudiensis
Fraser,
1931* |
Travancore Bambootail |
DD |
✔ |
— |
✔ |
— |
— |
— |
— |
— |
— |
— |
— |
|
78 |
Prodasineura verticalis (Selys, 1860) |
Red-striped Black Threadtail |
LC |
✔ |
✔ |
✔ |
✔ |
✔ |
— |
— |
— |
— |
✔ |
— |
|
79 |
Onychargia atrocyana (Selys, 1865) |
Black Marsh Dart |
LC |
— |
— |
— |
— |
✔ |
— |
— |
— |
— |
— |
— |
|
|
Family: Platystictidae
Kennedy, 1920 |
|||||||||||||
|
80 |
Protosticta gravelyi Laidlaw, 1915* |
Pied Shadow Damsel |
LC |
✔ |
— |
✔ |
— |
— |
— |
— |
— |
— |
✔ |
— |
|
81 |
Protosticta rufostigma Kimmins, 1958* |
- |
DD |
✔ |
— |
— |
— |
— |
— |
— |
— |
— |
— |
— |
|
82 |
Protosticta sanguinostigma Fraser, 1922* |
Red Spot Reedtail |
VU |
— |
— |
✔ |
— |
— |
— |
— |
— |
— |
— |
— |
For
figures & images - - click here for full PDF
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