Journal of Threatened
Taxa | www.threatenedtaxa.org | 26 March 2025 | 17(3): 26697–26703
ISSN 0974-7907 (Online)
| ISSN 0974-7893 (Print)
https://doi.org/10.11609/jott.9390.17.3.26697-26703
#9390 | Received 30
December 2024 | Final received 06 March 2025 | Finally accepted 10 March 2025
Preliminary checklist
of avifauna from All India Institute of Medical Sciences, Guwahati, Assam,
India
Nitul Ali 1, Vivek Chetry 2, Prem Kishan Singha 3 &
Maina Boro 4
1,3 Department of
Zoology, Rangia College, Rangia,
Kamrup, Assam 781354, India.
2 Animal Ecology and
Wildlife Biology Laboratory, Department of Zoology, Gauhati
University, Guwahati, Assam 781014, India.
4 West Guwahati College
of Education, Pandu, Guwahati, Assam 781012, India.
1 zoology.nitulali@gmail.com
(corresponding author),2 vivekchetry127@gmail.com, 3 dr.premkishansingha@gmail.com,
4 mainaboro941@gmail.com
Editor: S. Balachandran, Bombay Natural History
Society, Mumbai, India. Date of publication: 26 March 2025
(online & print)
Citation: Ali, N., V. Chetry, P.K. Singha & M. Boro (2025).
Preliminary checklist of avifauna from All India Institute of Medical Sciences,
Guwahati, Assam, India. Journal of Threatened
Taxa 17(3): 26697–26703. https://doi.org/10.11609/jott.9390.17.3.26697-26703
Copyright: © Ali et al. 2025. 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: None.
Competing interests: The authors declare no competing interests.
Author details: Nitul Ali is an assistant professor in the Department of Zoology at Rangia College. His research interests include regional biodiversity, biochemistry, microbiology and animal physiology. Vivek Chetry is a research scholar at the Department of Zoology, Gauhati University, specializing in avian ecology. His research explores bird diversity, habitat associations, and conservation strategies. Prem Kishan Singha is an assistant professor and currently working as the Head in the Department of Zoology, Rangia College. He is interested in ecological interactions, species conservation and animal physiology. Maina Boro works as an assistant professor at West Guwahati College of Education and is actively involved in science education and promoting environmental awareness.
Author contributions: NA and VC conceptualized the study and designed the methodology. NA, VC, and MB were involved in data collection and analysis, ensuring the accuracy and reliability of the results. All authors (NA, VC, PKS, and MB) participated in writing, reviewing, and editing
the manuscript. All authors have read and approved the final version of the manuscript.
Abstract: Bird diversity in
various types of habitats, including institutional campuses, underlines the
importance of these green areas for preserving ecological integrity and
providing necessary havens for avian species. The present study presents the
first preliminary checklist of avifaunal species within the AIIMS Guwahati
campus. A total of 75 bird species were recorded in this study from April 2024
to July 2024. Fifty species were observed in wetland habitat and 40 in built-up
areas, with 15 species occurring in both habitats. About 73 species are
classified as ‘Least Concern’, and two as ‘Near Threatened’, according to the
IUCN Red List. The present study highlights the importance of natural habitats
like wetlands, which are more favourable for bird
foraging and nesting than built-up areas.
Keywords: AIIMS, birds,
built-up land, campus, greenspace, habitat connectivity, Kamrup,
Near Threatened, point count, wetland.
Introduction
Avian
diversity on built-up land provides insights into the ecological health of the
region (Latta et al. 2013; Bajagain
et al. 2020). Avifaunal diversity observed within an institute’s premises
highlights the importance of maintaining suitable habitats for birds, as they
fulfil numerous ecological functions, serve as bioindicators and contribute to
migration and adaptation processes (Rajashekara &
Venkatesha 2017). Their presence and diversity can be
used to assess the environmental quality of the institute’s surroundings.
Assam,
a northeastern state of India, is known for its rich and diverse avifaunal
population. The region’s unique geographic location, encompassing the eastern
Himalaya and the Brahmaputra River basin, provides a habitat for many birds. Assam
is home to around 700 bird species in recognised
Important Bird and Biodiversity Areas (IBAs), and also in urban and semi-urban
settings including institutional campuses (Rahmani et
al. 2016; Bhaduri & Rathod 2022; BirdLife International 2022). Research has shown that
educational campuses host significant avian diversity, with surveys reporting
an average of 66 to 88 bird species per campus, including some threatened
species (Devi et al. 2012; Aggarwal et al. 2015; Chakdar
et al. 2016; Liu et al. 2021; Guthula et al. 2022;
Kumar et al. 2024; Singh et al. 2024). These campuses serve as significant
habitats for birds due to their abundant greenery, food resources, and
relatively low levels of disturbance (Bhaduri &
Rathod 2022).
The
All India Institute of Medical Sciences (AIIMS) in Guwahati, situated near
significant birding sites like Deepor Beel Wildlife Sanctuary, Dighali Beel, and Jendia Beel, is a potential habitat for birds. This study is
focused on documenting the avian diversity within the AIIMS Guwahati campus.
Materials and Method
Study
area
Bird
observations were conducted in and around the All India Institute of Medical
Sciences (AIIMS), Guwahati. The institute is located at 26.253 °N and 91.696 °E
in Changsari, a locality of Kamrup
District, Assam, and spans 189.2 ac (Image 1). The campus features built-up
land featuring the hospital, institute and residential campus with newly
created green space. A significant portion of the campus includes a marshy
wetland habitat that spans around 85 ac, while the built-up urban area is
approximately 95 ac. The marsh areas are mainly composed of rooted vegetation
such as Nymphaea stellata, Pontederia
hastata and free-floating plants like Eichhornia crassipes.
The nearest forest, Dirgheswari Reserve Forest, a
moist deciduous hill forest, is about 1.5 km to the northeastern side of the
campus.
Data
collection
This
study was carried out from April 2024 to July 2024. The point count method was
used, which lasted 15 min per point count (Drapeau et al. 1999). As the primary
goal of the study was to record the list of species, a point count with an
unlimited radius was used (Bibby et al. 2000). All birds observed and heard
were noted. Most observations were conducted in the morning between 0600 h and
0900 h, except a few in the evening (between 1500 h and 1700 h) to count some
species that usually roost in marshy wetlands. Field surveys were undertaken
twice a week from April to July. Birds encountered during other than census
period were also considered during the study. Birds were observed using a pair
of binoculars (Nikon 8 × 40), and field identification was done based on Grimmett et al. (2016). Taxonomy was followed as per
Clements Checklist v2023 (Clements et al. 2023).
Results
During
the study period, 75 species belonging to 16 orders and 42 families of birds
were observed (Table 1). Among the recorded species, 29 were passerine, while
44 were non-passerine. Among the 42 families, the highest species (6 species)
belonged to the Ardeidae family. The point count
surveys recorded an average of 7.5 ± 2.4 (mean ± SD) species per survey. According
to the IUCN Red List, 73 species are listed as Least Concern, while two
species, namely Lesser Adjutant Leptoptilos
javanicus, and Oriental Darter Anhinga
melanogaster, are classified as Near Threatened.
Among
the two Near Threatened species observed, the Lesser Adjutant had the highest
count, with a maximum of three individuals recorded in a single survey. This
was followed by the Oriental Darter, with two individuals. Two winter migratory
species, Dusky Warbler Phylloscopus fuscatus and Brown Shrike Lanius
cristatus were also observed in the wetland
habitat during the study. Higher numbers of species (n = 50) were observed
in the wetland habitat relative to built-up land (n = 40), and 15 species were
observed in both habitats (Figure 1).
Discussion
The wetland habitat
on the AIIMS Guwahati campus supports a greater diversity of bird species
compared to built-up areas, primarily due to its varied vegetation, including
tall grasses (e.g., Saccharum sp.),
free-floating plants like Water Hyacinth Pontederia
crassipes, rooted aquatic species such as Lotus Nelumbo nucifera, and abundant food
resources. This rich habitat attracts bird species, including the Chestnut
Munia Lonchura atricapilla,
Grey-headed Swamphen Porphyrio
poliocephalus, and Bronze-winged Jacana Metopidius indicus, which use the area for
nesting, foraging, and roosting. Numerous studies have highlighted the
importance of wetlands in supporting high bird species richness (Zhu & Wang
2022; Cristaldi et al. 2023; Zhang et al. 2023).
Also, wetlands, the transition between terrestrial and aquatic habitats, often
host a wide array of resident and migratory bird species (Khatri et al. 2019).
The presence of two near-threatened species of waterbirds
in the campus wetlands is particularly noteworthy, as it highlights the
biodiversity value of these habitats and the need for their conservation to
safeguard the regional avifauna (Kumdet et al. 2021).
Low species number in
the campus might be due to the newly-constructed built-up land, as they often
lack tree cover, which results in the loss of vital nesting and foraging
habitat for birds (Bajagain et al. 2020).
Additionally, the short duration of the study, which did not cover the winter
season, might have contributed to the observed lower species number, as some
migratory bird species are present during specific times of the year. Similar
results were also obtained on the campuses of the Indian Institute of
Technology, Guwahati (Bhaduri & Rathod 2022) and
Assam University (Chakdar et al. 2016). As the AIIMS
campus was constructed on a wetland, many common urban bird species such as
Rufous Treepie Dendrocitta vagabunda, Large-billed Crow Corvus
macrorhynchos and Black-rumped
Flameback Dinopium
benghalense were missing during the study period.
The ongoing green space landscaping might attract those species in future once
there is sufficient tree cover to support them.
Studies have shown
that institutional campuses with well-developed greenspaces can support a
surprising diversity of avifauna, likely due to the availability of suitable
habitat features such as vegetation cover, water sources, and reduced
disturbance (Mardiastuti 2020). Understanding the
factors that shape bird distribution in wetland and urban greenspace
environments is crucial for informing effective conservation strategies.
Habitat size, connectivity, and vegetation composition are identified as
critical drivers of avian diversity in urban greenspaces (Aronson et al. 2014).
The expansion of built-up areas can lead to a decline in bird diversity, as
urbanisation often results in the fragmentation and loss of natural habitats
that are essential for the survival and reproduction of many avian species.
Newly created built-up land with planned green space can gradually attract more
birds and support higher bird diversity over time, as seen in some
institutional campuses, provided the green spaces are well-designed and
maintained (Ibáñez-Álamo et al. 2020; Kumdet et al. 2021). Such landscapes play a vital role in
supporting biodiversity in urban areas.
To conserve the
existing wetland habitat on campus, it is essential to maintain water quality
by controlling pollution and managing runoff from the built-up areas.
Sustainable campus management practices, such as increasing green spaces and
reducing impervious surfaces, which minimise environmental impact and support
habitat conservation. Additionally, planting native trees including fig (Banyan
and other Ficus species) can promote bird diversity
by providing essential food sources and nesting habitats (Caughlin
et al. 2012). Creating green corridors that link the marshland areas to the
nearby Dirgheswari Reserve forest can promote
biodiversity and enhance habitat connectivity for birds and smaller fauna.
Table 1. List of
avian species observed from AIIMS, Guwahati campus. B—Built-up land | W—Wetland
| IUCN— International Union for Conservation of Nature | LC—Least Concern |
NT—Near Threatened.
|
|
Order / Family/ Scientific name |
Common name |
IUCN Red List
status |
Habitat |
|
|
|
Anseriformes |
|
|||
|
|
Anatidae |
|
|||
|
1 |
Dendrocygna javanica |
Lesser Whistling
Duck |
LC |
W |
|
|
|
Columbiformes |
|
|||
|
|
Columbidae |
|
|||
|
2 |
Streptopelia chinensis |
Spotted Dove |
LC |
B |
|
|
3 |
Streptopelia tranquebarica |
Red Collared-Dove |
LC |
B |
|
|
4 |
Streptopelia decaocto |
Eurasian
Collared-Dove |
LC |
B |
|
|
5 |
Columba livia |
Rock Pigeon |
LC |
B |
|
|
|
Cuculiformes |
|
|||
|
|
Cuculidae |
|
|||
|
6 |
Centropus bengalensis |
Lesser Coucal |
LC |
W |
|
|
7 |
Centropus sinensis |
Greater Coucal |
LC |
W |
|
|
8 |
Hierococcyx varius |
Common Hawk-Cuckoo |
LC |
W |
|
|
9 |
Eudynamys scolopaceus |
Asian Koel |
LC |
B, W |
|
|
10 |
Cacomantis merulinus |
Plaintive Cuckoo |
LC |
W |
|
|
|
Caprimulgiformes |
|
|||
|
|
Apodidae |
|
|||
|
11 |
Cypsiurus balasiensis |
Asian Palm-Swift |
LC |
B, W |
|
|
|
Gruiformes |
|
|||
|
|
Rallidae |
|
|||
|
12 |
Amaurornis phoenicurus |
White-breasted
Waterhen |
LC |
W |
|
|
13 |
Gallinula chloropus |
Eurasian Moorhen |
LC |
W |
|
|
14 |
Porphyrio poliocephalus |
Grey-headed Swamphen |
LC |
W |
|
|
|
Charadriiformes |
|
|||
|
|
Charadriidae |
|
|||
|
15 |
Vanellus indicus |
Red-wattled Lapwing |
LC |
W |
|
|
|
Jacanidae |
|
|
|
|
|
16 |
Metopidius indicus |
Bronze-winged
Jacana |
LC |
W |
|
|
17 |
Hydrophasianus chirurgus |
Pheasant-tailed
Jacana |
LC |
W |
|
|
|
Ciconiiformes |
|
|||
|
|
Ciconiidae |
|
|||
|
18 |
Anastomus oscitans |
Asian Openbill
Stork |
LC |
W |
|
|
19 |
Leptoptilos javanicus |
Lesser Adjutant |
NT |
W |
|
|
|
Suliformes |
|
|||
|
|
Anhingidae |
|
|||
|
20 |
Anhinga
melanogaster |
Oriental Darter |
NT |
W |
|
|
|
Phalacrocoracidae |
|
|||
|
21 |
Microcarbo niger |
Little Cormorant |
LC |
W |
|
|
|
Pelecaniformes |
|
|||
|
|
Ardeidae |
|
|||
|
22 |
Ardea purpurea |
Purple Heron |
LC |
W |
|
|
23 |
Ardea intermedia |
Medium Egret |
LC |
W |
|
|
24 |
Ardeola grayii |
Indian Pond Heron |
LC |
W |
|
|
25 |
Bubulcus ibis |
Cattle Egret |
LC |
B, W |
|
|
26 |
Nycticorax nycticorax |
Black-crowned
Night-Heron |
LC |
W |
|
|
27 |
Ixobrychus cinnamomeus |
Cinnamon Bittern |
LC |
W |
|
|
|
Threskiornithidae |
|
|||
|
28 |
Threskiornis melanocephalus |
Black-headed Ibis |
LC |
W |
|
|
29 |
Plegadis falcinellus |
Glossy Ibis |
LC |
W |
|
|
|
Accipitriformes |
|
|||
|
|
Accipitridae |
|
|||
|
30 |
Elanus caeruleus |
Black-winged Kite |
LC |
B |
|
|
31 |
Milvus migrans |
Black Kite |
LC |
W |
|
|
32 |
Pernis ptilorhynchus |
Oriental
Honey-buzzard |
LC |
W |
|
|
33 |
Spilornis cheela |
Crested
Serpent-Eagle |
LC |
B, W |
|
|
34 |
Hieraaetus pennatus |
Booted Eagle |
LC |
B, W |
|
|
|
Strigiiformes |
|
|||
|
|
Strigidae |
|
|||
|
35 |
Athene brama |
Spotted Owlet |
LC |
B |
|
|
|
Bucerotiformes |
|
|||
|
|
Upupidae |
|
|||
|
36 |
Upupa epops |
Eurasian Hoopoe |
LC |
B |
|
|
|
Coraciiformes |
|
|||
|
|
Alcedinidae |
|
|||
|
37 |
Halcyon smyrnensis |
White-throated
Kingfisher |
LC |
B, W |
|
|
38 |
Alcedo atthis |
Common Kingfisher |
LC |
W |
|
|
|
Meropidae |
|
|
|
|
|
39 |
Merops leschenaulti |
Chestnut-headed
Bee-eater |
LC |
B |
|
|
40 |
Merops orientalis |
Green Bee-eater |
LC |
B |
|
|
|
Coraciidae |
|
|
|
|
|
41 |
Coracias affinis |
Indochinese Roller |
LC |
B |
|
|
|
Piciformes |
|
|
|
|
|
|
Megalaimidae |
|
|
|
|
|
42 |
Psilopogon asiaticus |
Blue-throated
Barbet |
LC |
B |
|
|
43 |
Psilopogon lineatus |
Lineated Barbet |
LC |
B |
|
|
|
Picidae |
|
|
|
|
|
44 |
Dendrocopos macei |
Fulvous-breasted
Woodpecker |
LC |
B |
|
|
|
Psittaciformes |
|
|||
|
|
Psittaculidae |
|
|||
|
45 |
Psittacula krameri |
Rose-ringed
Parakeet |
LC |
B |
|
|
|
Passeriformes |
|
|||
|
|
Oriolidae |
|
|||
|
46 |
Oriolus xanthornus |
Black-hooded Oriole |
LC |
B |
|
|
|
Artamidae |
|
|
|
|
|
47 |
Artamus fuscus |
Ashy Wood Swallow |
LC |
B, W |
|
|
|
Aegithinidae |
|
|
|
|
|
48 |
Aegithina tiphia |
Common Iora |
LC |
B, W |
|
|
|
Dicruridae |
|
|
|
|
|
49 |
Dicrurus macrocercus |
Black Drongo |
LC |
B, W |
|
|
|
Laniidae |
|
|
|
|
|
50 |
Lanius cristatus |
Brown Shrike |
LC |
W |
|
|
51 |
Lanius schach |
Long-tailed Shrike |
LC |
W |
|
|
|
Corvidae |
|
|||
|
52 |
Corvus splendens |
House Crow |
LC |
B |
|
|
|
Paridae |
|
|||
|
53 |
Parus cinereus |
Cinereous Tit |
LC |
B |
|
|
|
Alaudindae |
|
|||
|
54 |
Alauda gulgula |
Oriental Skylark |
LC |
B, W |
|
|
55 |
Mirafra assamica |
Bengal Bushlark |
LC |
W |
|
|
|
Cisticolidae |
|
|
|
|
|
56 |
Orthotomus sutorius |
Common Tailorbird |
LC |
B |
|
|
57 |
Prinia inornata |
Plain Prinia |
LC |
W |
|
|
|
Hirundinidae |
|
|||
|
58 |
Hirundo rustica |
Barn Swallow |
LC |
W |
|
|
|
Pycnonotidae |
|
|||
|
59 |
Pycnonotus cafer |
Red-vented Bulbul |
LC |
B, W |
|
|
|
Phylloscopidae |
|
|||
|
60 |
Phylloscopus fuscatus |
Dusky Warbler |
LC |
W |
|
|
|
Timaliidae |
|
|||
|
61 |
Turdoides striata |
Jungle Babbler |
LC |
B |
|
|
|
Locustellidae |
|
|||
|
62 |
Megalurus palustris |
Striated Grassbird |
LC |
W |
|
|
|
Sturnidae |
|
|||
|
63 |
Gracupica contra |
Asian Pied Starling |
LC |
W |
|
|
64 |
Acridotheres tristis |
Common Myna |
LC |
B |
|
|
65 |
Acridotheres fuscus |
Jungle Myna |
LC |
B |
|
|
66 |
Acridotheres grandis |
Great Myna |
LC |
B, W |
|
|
|
Muscicapidae |
|
|||
|
67 |
Copsychus saularis |
Oriental Magpie
Robin |
LC |
B |
|
|
|
Nectariniidae |
|
|
|
|
|
68 |
Aethopyga siparaja |
Crimson Sunbird |
LC |
B |
|
|
69 |
Cinnyris asiaticus |
Purple Sunbird |
LC |
B, W |
|
|
|
Ploceidae |
|
|
|
|
|
70 |
Ploceus philippinus |
Baya Weaver |
LC |
W |
|
|
|
Estrildidae |
|
|||
|
71 |
Lonchura punctulata |
Scaly-breasted
Munia |
LC |
B, W |
|
|
72 |
Lonchura atricapilla |
Chestnut Munia |
LC |
B, W |
|
|
|
Passeridae |
|
|||
|
73 |
Passer domesticus |
House Sparrow |
LC |
B |
|
|
74 |
Passer montanus |
Eurasian Tree
Sparrow |
LC |
B |
|
|
|
Motacillidae |
|
|||
|
75 |
Anthus rufulus |
Paddyfield Pipit |
LC |
W |
|
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