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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