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

 

 

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