Journal of Threatened Taxa | www.threatenedtaxa.org | 26 July 2026 | 18(7): 29322–29330

 

ISSN 0974-7907 (Online) | ISSN 0974-7893 (Print) 

https://doi.org/10.11609/jott.9438.18.7.29322-29330

#9438 | Received 28 September 2024 | Final received 01 January 2025| Finally accepted 01 May 2026

 

 

A checklist of the avifauna of the Noakhali Science and Technology University campus, Noakhali, Bangladesh

 

Ashikur Rahman Jibon 1, Tanzina Alam 2  & M. Rakibur Rahman 3        

 

1,2,3 Department of Zoology, Noakhali Science and Technology University, Noakhali 3814, Bangladesh.

1 ashikurrahmanj029@gmail.com, 2 tanzina@nstu.edu.bd (corresponding author), 3 rakiburrahman8575@gmail.com

 

 

Editor: H. Byju, Coimbatore, Tamil Nadu, India.               Date of publication: 26 July 2026 (online & print)

 

Citation: Jibon, A.R., T. Alam & M.R. Rahman (2026). A checklist of the avifauna of the Noakhali Science and Technology University campus, Noakhali, Bangladesh. Journal of Threatened Taxa 18(7): 29322–29330. https://doi.org/10.11609/jott.9438.18.7.29322-29330

  

Copyright: © Jibon 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: No funding received.

 

Competing interests: The authors declare no competing interests.

 

Author details: Ashikur Rahman Jibon is a graduate of the Department of Zoology and is currently pursuing MS in Wildlife Biology at Noakhali Science and Technology University, Bangladesh. His academic interests include wildlife ecology, biodiversity conservation, ornithology, and environmental science. Tanzina Alam is a faculty member at the Department of Zoology, Noakhali Science and Technology University, Bangladesh. Her research interests include avian ecology, biodiversity conservation, coastal ecosystems, and wildlife monitoring. Md. Rakibur Rahman is a graduate of the Department of Zoology and is currently pursuing MS in Fisheries and Limnology at Noakhali Science and Technology University, Bangladesh. He is interested in biodiversity assessment, conservation, and ecological field research.

 

Author contribution: ARJ and TA conceptualized and designed the study. ARJ and MRR conducted the field surveys and compiled the data. ARJ and TA analyzed the data and prepared the manuscript. All authors reviewed and approved the final manuscript.

 

 

Abstract: A study was conducted on the avifauna of the Noakhali Science and Technology University (NSTU) campus, Noakhali, Bangladesh, from October 2023 to July 2024. Ninety species of birds belonging to 44 families and 13 orders were identified, of which 51 species were non-passerines, and 39 species were passerines. Among the birds, 73 species were residents, 12 species were winter visitors, four species were recorded as both residents and winter visitors, and one species was a passage migrant. Of the recorded birds, three species were very common, six species were common, 18 species were uncommon, 35 species were few, and 28 species were rare. The local status of these birds in NSTU has also been compared with their national status in Bangladesh. Anthropogenic activities such as human interventions, construction projects, pollution, agriculture, and deforestation were prevalent at the NSTU campus, posing potential threats to birds. Therefore, it is essential to implement appropriate measures to conserve this unique habitat.

 

Keywords: Anthropogenic activities, birds, habitat fragmentation, Lesser Whistling Duck, point count, relative frequency.

 

 

INTRODUCTION

 

Bangladesh has rich plant and animal diversity because of its fertile soil and moderate climatic conditions.  The sub-tropical monsoon climate shows three climatological seasons: pre-monsoon (hot) March to May; monsoon (rainy season) - June to October, and winter (dry) - November to February (Ahmad 1968). Bangladesh, covering a land mass of 147,570 km2, has 650 bird species; of these, 302 are residents, 176 are seasonal visitors, and 143 are vagrants (Siddiqui et al. 2008).

One of the most important ecological indicators for determining habitat quality, maintaining the trophic level, and evaluating the general health of an ecosystem is the diversity of avifauna (Whelan et al. 2008; Mathibalan et al. 2026). They are highly susceptible to changes in the habitat in which they live due to people’s disrespect for their protection and conservation (Sarker et al. 2001). Birds provide all four categories of ecological services: provisioning, regulating, cultural, and supporting (Whelan et al. 2008). Through the services offered by birds, they indirectly and directly benefit humans as bio-indicators, pollinators, seed dispersers, predators, scavengers, and ecosystem engineers (Sekercioglu 2006; Wenny et al. 2011).

The diversity of avifauna in different educational institution campuses of Bangladesh has been studied by many authors. Mohsanin & Khan (2009) worked on the status and seasonal occurrence of the birds in Jahangirnagar University Campus, Dhaka; whereas Reza et al. (2012) recorded the birds of the Rajshahi University Campus, Rajshahi. Chowdhury et al. (2014) conducted a study on the checklist of avian fauna of the Dhaka University Campus, Dhaka; while Kabir et al. (2017) documented a checklist of the avian fauna of the Chittagong University campus, Chittagong.

Noakhali Science and Technology University (NSTU) is a notable habitat for plants and birds.  This habitat functions as a feeding, resting and breeding ground for many birds. In addition to birds, various amphibians, reptiles and mammals are also observed in this habitat. However, no recent work has been done on the avifauna of the NSTU campus. So, the present work was undertaken to list the avifauna of the NSTU campus with special reference to their country status, relative frequency and anthropogenic threats, which will provide some basic information for future investigation and conservation of the birds in the NSTU campus.

 

 

MATERIALS AND METHODS

 

STUDY AREA

NSTU is a public university in the coastal terrain of Noakhali, Bangladesh. It is situated at Sonapur, Noakhali Sadar Upazila, which is 8 km south of Maijdee Town (22.792o N, 91.102o E; Image 1). The NSTU campus covers a land area of 101 ac (0.41 km2). The total area constitutes 5% permanent wetlands, 10% seasonal wetlands , 15% agricultural lands, 5% playgrounds, 35% constructed storied building sites, and 30% other areas. This area is adorned with beautiful natural resources. Both indigenous and exotic plant species inhabit this area. The study area is covered with a wide variety of trees like Haritaki Terminalia chebula, Koroi Albizia procera, Jarul Legestroemia speciosa, Jhau Tamarix dioica, Sissu Dalbergia sissoo, Mandar Erythrina variegate, Banyan Ficus benghalensis, and Acacia Acacia auriculiformis. Fruit-bearing plants, such as Mango Mangifera indica, Jackfruit Artocarpus heterophylus, Coconut Cocos nucifera, Boroi Zizyphus mauritiana, Banana Musa acuminata, and Papaya Carica papaya are also seen in this area. In the agricultural lands, different types of crops are cultivated, such as, Rice Oryza sativa and Sunflower Helianthus sp. There are some experimental plots in which Watermelon Citrullus lanatus, Dragon Fruit Selenicereus sp., Chilli Capsicum sp., Carrot Daucus carota, and Tomato Solanum lycopersicum are cultivated.

The area is under a tropical climate, and it has significant rainfall most months, with a short dry season. The monthly temperature, humidity and precipitation were varied during the study period. May recorded the highest temperature at (41°C), while the lowest temperature (18°C) was observed in January; the maximum humidity (80%) was in July and the minimum (52%) in February. July experienced its highest level of precipitation, reaching 671 mm.

 

Methods

The study was conducted from October 2023 to July 2024. Bird surveys were conducted on four days per month. The timing of the fieldwork was selected based on the visibility of avian species. A total of 40 days were spent bird-watching throughout the study period. In addition to that some human disturbances were also documented during the present study.

Regular surveys were conducted along existing roads and walking trails of the NSTU campus from 0700–1700 h. Birds were surveyed using point count method, with a distance of 100 m between adjacent points (Bibby et al. 2000). The duration at each point for counting signs, recording calls, and observing birds was 5 min. Bushnell (10x42) binocular was used to observe bird species. Whenever a bird called, flew, moved around plants and trees, or nested on a tree or bushes, pictures and video clips were taken whenever feasible to identify birds accurately at the generic and species level. Opportunistic sightings were also included in the checklist. The recorded birds were identified with the help of the books (Siddiqui et al. 2008; Grimmett et al. 2021).

The relative frequency of the available bird species has been assessed as very common (VC): seen during 80–100 % of the field visits; common (C): found during 50–79 % of the field visits; uncommon (UC): observed during 20–49 % of the field visits; few (F): met less than 19% field visits and rare (R): found occasionally (Khan 1982; Kabir et al. 2017). All the avian species have been categorized as residents, winter migrants, resident and winter migrants, and passage migrants following Siddiqui et al. (2008).

 

RESULTS

 

Species composition

Ninety species of birds representing 44 families and 13 orders were observed from the NSTU campus during October 2023–July 2024; of which 51 (56.67%) species were non-passerine and 39 (43.33%) passerine (Table 1). Among the recorded 90 species of birds, 25 species are water birds. The resident birds represented the major composition (73 species, i.e., 81.11%) in the campus and passage migrants constituted the lowest proportion (1 species, i.e., 1.11%) (Image 3). Among the orders, Passeriformes constituted the highest number (39 species, i.e., 43.33%) and three orders (Suliformes, Apodiformes and Anseriformes) represented one (1.11%) species each (Table 1; Image 2).

Among the 44 families, Ardeidae had the dominating number, nine species (10%) of Rallidae five species (5.55%); Sturnidae, Cuculidae, Columbidae, and Picidae had four species (4.44%) each; Corvidae, Dicruridae, Nectariniidae, Estrildidae, Cisticolidae, Accipitridae, Alcedinidae, and Charadriidae had three species (3.33%) each; Muscicapidae, Motacillidae, Megalaimidae, Scolopacidae, and Strigidae had two species (2.22%) each; and all rest of the families had one species (1.11%) (Table 1).

 

Relative frequency

Frequency of observation showed that three species were very common, six species were common, 18 species were uncommon, 35 species were few and 29 species were rare. The status of these birds in NSTU has also been compared with the country’s status (Image 3).

Species classified under the few category constituted the largest proportion of the assemblage, accounting for 38.89% (35 species), and the very common species represented the lowest (3.33%, 3 species) in the NSTU (Image 4). The Black Drongo Dicrurus macrocercus, Oriental Magpie-Robin Copsychus saularis and Red-vented Bulbul Pycnonotus cafer were recorded as very common bird species.

 

Problems and threats

The anthropogenic activities such as habitat fragmentation, construction and infrastructure development, destruction of habitat, pollution, agricultural intensification, overuse of agrochemicals, and subsistence hunting of birds have been documented to negatively impact birds and their activity patterns in the study area. Water, sound and plastic pollution, pesticides, and heavy metals harm birds directly and indirectly. Pesticides can be toxic, and birds often ingest plastics or get entangled in them. Structural development, agriculture, deforestation, grass and reed burning and other land use changes directly destroy the natural habitats of birds. These activities impacted birds through habitat fragmentation. Direct human threats like poaching, hunting, stone throwing, etc., also harm water and forest birds. Because it is still evolving, the avifauna has a hard time figuring out where to nest, where to hide, or how to feed in this area. These problems might be affecting the bird species in the study area.

 

 

DISCUSSION

 

The NSTU campus, despite its small area, has a rich avian diversity.  The study recorded 90 species, of which 25 species (27.78%) are waterbirds.  It indicates that the wetlands of the study area are suitable as a foraging ground for the water birds. Compared to other major university campuses in Bangladesh, NSTU’s diversity is competitive given its size. Previous studies have documented varying richness across the country.  Rajshahi University campus observed a total of 159 species of birds across 36 families (Reza et al. 2012), whereas Chittagong University (CU) recorded 215 species across 63 families (Kabir et al. 2017).  Dhaka University recorded 54 to 70 species recorded in different periods (Banu et al. 2016; Shome et al. 2022), and Jahangirnagar University documented 78 species (Chowdhury et al. 2014) and 92 species (Ahsan & Khanom 2005).

Both resident and migratory birds were documented in the study area. Among them, the majority were residents. Brown Crake Zapornia akool, a rare bird (Grimmett et al. 2021) reported from the study area, is known as a former resident of Bangladesh (Siddiqui et al. 2008). From the Rajshahi University campus, Reza et al. (2012) observed 121 species of residents and 38 species of migratory birds; whereas Banu et al. (2016) reported 10 (19%) species as migrants and 44 (81%) as residents in the Dhaka University campus. According to Kabir et al. (2017), 74.42% of resident birds and 25.58% of local and seasonal migrants were observed in the Chittagong University Campus. These findings mirror the trends observed in other academic landscapes.

For most of the species, the relative frequency was categorized as few, whereas the least number of species was categorized as very common. In the Rajshahi University campus, Reza et al. (2012) found very common (30 species), common (30 species), fairly common (34 species), few (32 species) and rare (34 species). From the Dhaka University campus, Banu et al. (2016) recorded 14 (26%) species as very common, 7 (13%) species as common, 10 (19%) species as uncommon, and 23 (43%) species as rare; while Kabir et al. (2017) recorded 101 species were very common, 36 species as common, 29 species as uncommon, 22 species as few and 27 as rare from the Chittagong University campus. The smaller size of the study area might have influenced the frequency of observation of the birds on the campus.

Anthropogenic activities refer to the actions or processes originating from human activity that impact the environment, ecosystems or natural resources and destroy biodiversity, including avian populations (Miller & Spoolman 2012; Manigandan et al. 2021). These activities are responsible for excessive habitat degradation, reduce nesting sites, destroy feeding grounds, affect overall activity patterns, and break the migration rhythm of diversified avifauna. The waterbirds belonging to the orders Anseriformes, Pelecaniformes, and Charadriiformes are mostly impacted due to human disturbances (Byju et al. 2025). The present study documented that these disturbances have contributed to the excessive decline of the Lesser Whistling Duck Dendrocygna javanica and affected their migration rhythm. Some bird species from the orders Passeriformes, Piciformes, and Columbiformes are also impacted by extreme human intervention.

These findings align with global and local concerns regarding habitat loss as the leading cause of avian extinction (Fahrig 2001). Similar trends of habitat loss due to human activity have been recorded on Hatiya Island (Hossain et al. 2004) and in urban spaces like Ramna Park (Rajia et al. 2015). Without targeted management to mitigate hunting, fishing, and noise pollution, the avian richness of the NSTU campus remains at risk of significant decline.

 

 

CONCLUSION

 

The current study suggests that the NSTU campus possesses a wealth of biodiversity and has the potential to become a habitat for birds. However, anthropogenic threats such as clearing trees, pollution and agricultural intensification in their natural habitat could affect the breeding and other behavioural activities of birds. Restoration of the habitat is necessary to support birds’ forage, shelter, and breeding to protect the avifauna of the NSTU campus. Key recommendations include planting fruit-bearing trees to attract several insectivorous and frugivorous birds to reside there. Consequently, in order to maintain the bird species and their population sustainability, awareness should be raised among the university’s faculty, staff and students about the need to protect these exquisite creatures.

 

 

Table 1. Observed bird species at the NSTU campus, Noakhali, Bangladesh.

 

 

Common name

Scientific name

Family

NSTU status

Relative frequency      (%)

Country status

 

Order: 1. Passeriformes

1

Rufous Treepie

Dendrocitta vagabunda (Latham, 1790)

1. Corvidae

F

10

Resident

2

Large-billed Crow

Corvus macrorhynchos (Wagler, 1827)

R

7.5

Resident

3

House Crow

Corvus splendens (Vieillot, 1817)

F

15

Resident

4

Black-hooded Oriole

Oriolus xanthornus (Linnaeus, 1758)

2. Oriolidae

UC

32.5

Resident

5

White-throated Fantail

Rhipidura albicollis (Vieillot, 1818)

3. Rhipiduridae

UC

32.5

Resident

6

Bronzed Drongo

Dicrurus aeneus (Vieillot, 1817)

4. Dicruridae

F

12.5

Resident

7

Black Drongo

Dicrurus macrocercus (Vieillot, 1817)

VC

82.5

Resident

8

Ashy Drongo

Dicrurus leucophaeus (Vieillot, 1817)

F

10

Winter visitor

9

Small Minivet

Pericrocotus cinnamomeus (Linnaeus, 1766)

5. Campephagidae

F

17.5

Resident

10

Common Iora

Aegithina tiphia (Linnaeus, 1758)

6. Aegithinidae

R

7.5

Resident

11

Barn Swallow

Hirundo rustica (Linnaeus, 1758)

7. Hirundinidae

R

7.5

Resident +Winter visitor

12

Oriental Magpie-Robin

Copsychus saularis (Linnaeus, 1758)

8. Muscicapidae

VC

85

Resident

13

Red-throated  Flycatcher

Ficedula albicilla (Pallas, 1811)

R

5

Winter visitor

14

Orange-headed Thrush

Geokichla citrina (Latham, 1790)

9. Turdidae

R

5

Resident

15

House Sparrow

Passer domesticus (Linnaeus, 1758)

10. Passeridae

C

60

Resident

16

White Wagtail

Motacilla alba (Linnaeus, 1758)

11. Motacillidae

F

10

Winter visitor

17

Citrine Wagtail

Motacilla citreola (Pallas, 1776)

R

5

Winter visitor

18

Baya Weaver

Ploceus philippinus (Linnaeus, 1766)

12. Ploceidae

F

12.5

Resident

19

Indian Pied Starling

Gracupica contra (Linnaeus, 1758)

13. Sturnidae

C

62.5

Resident

20

Chestnut-tailed Starling

Sturnus malabaricus (Gmelin, 1789)

 C

50

Resident

21

Jungle Myna

Acridotheres fuscus (Wagler, 1827)

F

10

Resident

22

Common Myna

Acridotheres tristis (Linnaeus, 1766)

F

17.5

Resident

23

Common Tailorbird

Orthotomus sutorius (Pennant, 1769)

14. Cisticolidae

UC

37.5

Resident

24

Plain Prinia

Prinia inornata (Sykes, 1832)

R

7.5

Resident

25

Dark-necked Tailorbird

Orthotomus atrogularis (Temminck, 1836)

F

12.5

Resident

26

Blyth’s Leaf Warbler

Phylloscopus reguloides (Blyth, 1842)

15. Phylloscopidae

F

12.5

Winter visitor

27

Blyth’s Reed Warbler

Acrocephalus dumetorum (Blyth, 1849)

16. Acrocephalidae

R

7.5

Winter Visitor

28

Red-vented Bulbul

Pycnonotus cafer (Linnaeus, 1766)

17. Pycnonotidae

VC

85

Resident

29

Red-whiskered Bulbul

Pycnonotus jocosus (Linnaeus, 1758)

R

7.5

Resident

30

Purple-rumped Sunbird

Leptocoma zeylonica (Linnaeus, 1766)

18. Nectariniidae

UC

22.5

Resident

31

Purple Sunbird

Cinnyris asiaticus (Latham, 1790)

F

10

Resident

32

Little Spiderhunter

Arachnothera longirostra (Latham, 1790)

R

5

Resident

33

Chestnut Munia

Lonchura atricapilla (Vieillot, 1807)

19. Estrildidae

UC

32.5

Resident

34

White-rumped Munia

Lonchura striata (Linnaeus, 1766)

UC

20

Resident

35

Scaly-breasted Munia

Lonchura punctulata (Linnaeus, 1758)

UC

25

Resident

36

Great Tit

Parus major (Linnaeus, 1758)

20. Paridae

F

10

Resident

37

Long-tailed Shrike

Lanius schach (Linnaeus, 1758)

21. Laniidae

UC

30

Resident

38

Common Woodshrike

Tephrodornis pondicerianus (Gmelin, 1789)

22. Vangidae

F

12.5

Resident

39

Indian White-eye

Zosterops palpebrosus (Temminck, 1824)

23. Zosteropidae

R

7.5

Resident

 

Order: 2. Cuculiformes

40

Asian Koel

Eudynamys scolopaceus (Linnaeus, 1758)

24. Cuculidae

F

10

Resident

41

Greater Coucal

Centropus sinensis (Stephens, 1815)

UC

35

Resident

42

Common Cuckoo

Cuculus canorus (Linnaeus,1758)

F

10

Passage migrant

43

Plaintive Cuckoo

Cacomantis merulinus (Scopoli, 1786)

R

5

Resident

 

Order: 3. Columbiformes

44

Rock Dove

Columba livia (Linnaeus, 1758)

25. Columbidae

UC

35

Resident

45

Eastern Spotted Dove

Spilopelia chinensis (Scopoli, 1786)

C

50

Resident

46

Eurasian Collared Dove

Streptopelia decaocto (Frivaldszky, 1838)

C

50

Resident

47

Red Collared Dove

Streptopelia tranquebarica (Hermann, 1804)

UC

42.5

Resident

 

Order: 4. Accipitriformes

48

Brahminy Kite

Haliastur indus (Boddaert, 1783)

26. Accipitridae

C

50

Resident

49

Black Kite

Milvus migrans (Boddaert, 1783)

F

 12.5

Resident

50

Grey-headed Fish Eagle

Icthyophaga ichthyaetus (Horsfield, 1821)

F

10

Resident

 

Order: 5. Pelecaniformes

51

Indian Pond Heron

Ardeola grayii (Sykes, 1832)

27. Ardeidae

UC

22.5

Resident

52

Little Egret

Egretta garzetta (Linnaeus, 1766)

UC

22.5

Resident

53

Inter mediate Egret

Ardea intermedia (Wagler, 1829)

F

12.5

Resident

54

Grey Heron

Ardea cinerea (Linnaeus, 1758)

R

5

Resident +Winter visitor

55

Great White Egret

Ardea alba (Linnaeus, 1758)

UC

22.5

Resident

56

Cinnamon Bittern

Ixobrychus cinnamomeus (Gmelin, 1789)

F

12.5

Resident

57

Cattle Egret

Bubulcus ibis (Linnaeus, 1758)

F

12.5

Resident

58

Yellow Bittern

Ixobrychus sinensis (Gmelin, 1789)

R

7.5

Resident

59

Purple Heron

Ardea purpurea (Linnaeus, 1766)

R

5

Resident

60

Glossy Ibis

Plegadis falcinellus (Linnaeus, 1766)

28. Threskiornithidae

R

5

Winter visitor

61

Asian Openbill

Anastomus oscitans (Boddaert, 1783)

29. Ciconiidae

F

10

Resident

 

Order: 6. Suliformes

62

Little Cormorant

Microcarbo niger (Vieillot, 1817)

30. Phalacrocoracidae

UC

22.5

Resident

 

Order: 7. Piciformes

63

Fulvous-breasted Woodpecker

Dendrocopos macei (Vieillot, 1818)

31. Picidae

F

12.5

Resident

64

Black-rumped Flameback

Dinopium benghalense (Linnaeus, 1758)

R

5

Resident

65

Common Flameback

Dinopium javanense (Ljungh, 1797)

R

5

Resident

66

Eurasian Wryneck

Jynx torquilla (Linnaeus, 1758)

R

2.5

Winter visitor

67

Lineated Barbet

Psilopogon lineatus (Vieillot,1816)

32. Megalaimidae

F

17.5

Resident

68

Blue-eared Barbet

Psilopogon cyanotis (Blyth, 1847)

F

10

Resident

 

Order: 8. Coraciiformes

69

Green Bee-eater

Merops orientalis (Latham, 1802)

33. Meropidae

UC

25

Resident

70

Common Kingfisher

Alcedo atthis (Linnaeus, 1758)

34. Alcedinidae

F

12.5

Resident

71

Stork-billed Kingfisher

Pelargopsis capensis (Linnaeus, 1766)

R

5

Resident

72

White-throated Kingfisher

Halcyon smyrnensis (Linnaeus, 1758)

F

10

Resident

73

Common Hoopoe

Upupa epops (Linnaeus, 1758)

35. Upupidae

F

10

Resident

 

Order: 9. Gruiformes

 

 

 

 

 

74

Brown Crake

Zapornia akool (Sykes, 1832)

36. Rallidae

F

10

Resident

75

White-breasted Waterhen

Amaurornis phoenicurus (Pennant, 1769)

UC

25

Resident

76

Grey-headed Swamphen

Porphyrio porphyrio (Linnaeus, 1758)

F

17.5

Resident

77

Common Moorhen

Gallinula chloropus (Linnaeus, 1758)

R

5

Resident

78

Eurasian Coot

Fulica atra (Linnaeus, 1758)

R

5

Winter visitor

 

Order 10. Charadriformes

 

 

 

 

 

79

Wood Sandpiper

Tringa glareola (Linnaeus, 1758)

37. Scolopacidae

F

10

Winter visitor

80

Common Sandpiper

Actitis hypoleucos (Linnaeus, 1758)

F

10

Winter visitor

81

Bronze-winged Jacana

Metopidius indicus (Latham, 1790)

38. Jacanidae

UC

30

Resident

82

Grey-headed Lapwing

Vanellus cinereus (Blyth, 1842)

39. Charadriidae

F

10

Winter visitor

83

Red-wattled Lapwing

Vanellus indicus (Boddaert, 1783)

F

10

Resident

84

Kentish plover

Charadrius alexandrinus (Linnaeus, 1758)

R

5

Winter visitor

85

Greater Painted Snipe

Rostratula benghalensis (Linnaeus, 1758)

40. Rostratulidae

 

R

5

Resident

 

Order: 11. Anseriformes

 

 

 

 

 

86

Lesser Whistling Duck

Dendrocygna javanica (Horsfield, 1821)

41. Anatidae

F

12.5

Resident +Winter visitor

 

Order: 12. Apodiformes

 

 

 

 

 

87

Asian Palm Swift

Cypsiurus balasiensis (Gray, 1829)

42. Apodidae

R

7.5

Resident

 

Order: 13. Strigiformes

 

 

 

 

 

88

Spotted Owlet

Athene brama (Temminck, 1821)

43. Strigidae

R

5

Resident

89

Brown Boobook

Ninox scutulata (Raffles, 1822)

R

5

Resident

90

Barn Owl

Tyto alba (Scopoli, 1769)

44. Tytonidae

R

5

Resident

VC—very common | C—common | UC—uncommon | F—few | R—rare.

 

For images - - click here for full PDF

 

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