Journal of Threatened Taxa |
www.threatenedtaxa.org | 26 May 2022 | 14(5): 20988–21001
ISSN 0974-7907
(Online) | ISSN 0974-7893 (Print)
https://doi.org/10.11609/jott.6705.14.5.20988-21001
#6705 | Received 13
September 2020 | Final received 05 December 2020 | Finally accepted 21 April
2022
A checklist of avifauna from
different habitats of semi-arid landscape in western parts (Mandsaur and Ratlam
districts) of Madhya Pradesh, India
Koushik Bhattacharjee 1 & Shuvadip Adhikari 2
1 Parbati Teachers’ Training
Institute, Chanda, Jamuria, Paschim Bardhaman, West Bengal 713339, India.
2 Department of Zoology, The
University of Burdwan, Golapbag, Purba Bardhaman, West Bengal 713104, India.
1 koushik7777@gmail.com, 2 shuvaadhikari90@gmail.com
(corresponding author)
Editor: H. Byju, Coimbatore, Tamil Nadu,
India. Date of publication: 26 May
2022 (online & print)
Citation: Bhattacharjee, K. & S.
Adhikari (2022). A checklist of avifauna from
different habitats of semi-arid landscape in western parts (Mandsaur and Ratlam
districts) of Madhya Pradesh, India. Journal of Threatened Taxa 14(5): 20988–21001. https://doi.org/10.11609/jott.6705.14.5.20988-21001
Copyright: © Bhattacharjee & Adhikari 2022. 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: Koushik Bhattacharjee—MSc in conservation biology,
bird watcher and independent researcher.
Shuvadip Adhikari—PhD in
zoology, independent researcher and environmental activist, assistant editor of
‘Sudhu Sundarban Charcha’ a Bengali quarterly periodical.
Author contributions: Both of the authors were involved
in field survey, documentation, literature review and manuscript preparation,
editing and finalizing the manuscript.
Acknowledgements: We are thankful to anonymous
reviewers for their critical review and valuable suggestions.
Abstract: We prepared a checklist of avian
species recorded from two western districts (Mandsaur and Ratlam) of Madhya
Pradesh, situated in a semi-arid region with comments on their habitat
preference, feeding habits, migratory, and conservation status; 133 bird
species belonging to 47 families were recorded during the present study. About
30% of the species were migratory in status. In terms of habitat fidelity, 74
avian species were found only in a single habitat. Habitat-wise avian richness
varied widely. Among five habitats identified during the present study, wetland
supported the highest number (69) of avian species of which 58 species were
exclusively recorded from this habitat. Eight foraging guilds were identified
among which omnivores were dominant. Six
species of globally threatened and seven species of near-threatened species
were recorded during the present study. The presence of significant numbers of
winter migrants and globally threatened species indicated the importance, both
ecologically and biologically, of the semi-arid landscape for breeding and
migratory birds. Therefore, this work will provide baseline information to
conservationists for the development of conservation and management policies
for the two districts.
Keywords: Avian diversity, central India,
conservation, feeding habits, habitat fidelity, migratory, semi-arid landscape,
threatened species, wetlands, winter migrants.
Introduction
Birds are one of the most widely
distributed and abundant vertebrate taxa, living in diverse habitat types
across different ecosystems. In a particular ecosystem, the avian community
plays a variety of functional roles and provides different important ecosystem
services (Sekercioglu 2006, 2012; Whelan et al. 2008). Change in vegetation
composition affects the habitat quality for birds in terms of food, nesting
site, which in turn affect the species richness, abundance, and distribution (Western
& Grimsdell 1979). Birds generally colonize an area that is suitable in
terms of resources for their survival (Veech et al. 2011). Many species of
birds show fidelity towards a particular habitat (Chatterjee et al. 2013) so,
alteration or degradation of that particular habitat leads to a declining
population (Khan et al. 2019). Therefore, they act as an important bioindicator
of habitat quality, environmental degradation, pollution, and ecosystem health
(Gregory et al. 2003; Zhang & Ma 2011). Due to these essential ecological
functions, birds have always been extensively used for conservation and
environmental impact assessment studies (Knegtering et al. 2005).
Semi-arid regions are climatic
zones that are intermediate between humid and arid (desert) climates. This zone
is characterized by scanty precipitation and an aridity index between
0.20–0.50. Generally, the semi-arid region supports scrubby and grassland
vegetation along this region has agricultural potential (with proper irrigation
and management practices). Globally, about 65% of the area of total dry land in
the world comes under arid and semi-arid regions (FAO 1993). In India, the
semi-arid biogeographic zone is situated in transition between desert (arid)
and other zones like the Himalaya, Western Ghats, Deccan Peninsula, and
Gangetic plains (Rodgers & Panwar 1988). This region accounts for 16.60% of
the total geographic area of the country covering the states of Rajasthan,
Gujarat, Madhya Pradesh, Punjab, Haryana, Uttar Pradesh, and Maharashtra.
Two-hunderd-and-seventeen endemic bird areas (EBA) with a large number of
endemic bird species, identified by Birdlife International, are located within
the arid and semi-arid regions of the World (Stattersfield et al. 2005). Avian
populations in semi-arid regions are declining rapidly due to several factors
such as unplanned development activities, climate change, and urbanization.
Therefore, proper documentation of avian species, identification of their
habitats, and breeding grounds is essential for proper conservation and
management of avian communities and their habitat (Khan et al. 2019).
Avifaunal study in central India
started before independence with the earliest work by King in the year 1911 who
enlisted around 155 resident bird species from Saugar and Damoh (Chandra &
Singh 2004). Later several other studies in this field were conducted by
authors like Baker (1930a,b); D’Abreu (1931); Hewetson (1939), and Ali (1939,
1940). Grimmett & Inskipp (2003) listed 469 species of birds but due to lack
of a comprehensive study, Chandra & Singh (2004) undertook a literature
survey and reported around 488 taxa from Madhya Pradesh. In western Madhya
Pradesh, 139 avian species were reported from the Gandhisagar reservoir (Vyas
& Singh 2004) while Dange & Kumar (2013) listed 94 species of
birds from the Ratlam district.
Preparing a checklist of taxa is
the first and foremost task to acquire knowledge of biodiversity in a
particular geographic area. This checklist acts as a basis for further in-depth
studies, viz., systematics, taxonomy, distribution, evaluation, and
conservation (Núnez-Zapata et al. 2016). Keeping this in mind the main aim of
this study was to observe, record, and prepare a checklist of avian species
from two western districts of Madhya Pradesh, situated in the semi-arid region
with comments on their habitat preference, feeding habit, migratory and
conservation status.
Materials
and Methods
Study area
Mandsaur (Site I) and Ratlam
(Site II), two western districts of Madhya Pradesh located in the Malwa region
covers an area of 5,521 and 4,861 km2, respectively (Figure 1). The
climatic conditions of these two areas are generally dry except during the
monsoon season when it receives rainfall from the southwest monsoon. This area
is generally classified under a semi-arid biogeographical zone (Rodgers &
Panwar 1988). The average annual rainfall is 786 and 937 mm, respectively for
the sites. Summer temperature ranges 38–44 °C while the winter temperature
ranges 4–8 °C (Dange & Kumar 2013; NIC 2020).
We classified our study area into
five habitat types (Image 1) based on their vegetation type, land use, and land
cover which includes:
Wetland (WL): Both natural and
man-made wetlands are present in the study area that are home to a wide variety
of bird species that includes wintering and resident waterfowl, waders,
raptors, etc.
Grassland (GL): Dominated by
grass species of the genus Bothriochloa, Themeda, and Dichanthium
provide shelter to different raptors like Montagu’s Harrier, Short-toed Snake
Eagle, various passerines, and others.
Open scrub jungle (OS): Dominated
by Acacia and Balanities. Bird species inhabiting this area
include Shikra, Common Kestrel, dove, bushchat, bunting, and starling.
Agricultural land (AL): Several
crops like Soybean Glycine max, Wheat Triticum aestivum, Gram Cicer
arietinum, Mustard Brassica, and Maize Zea mays are
cultivated in this area.
Dry deciduous forest (DF): Most
of the forests covers in these two districts are mainly Tropical dry deciduous
forests which are dominated by Teak Tectona grandis and Butea sp.
mixed with other species like Saja Terminalia tomentosa, Sal Shorea
robusta, Bija Pterocarpus marsupium, Lendia Lagerstroemia parviflora,
Haldu Adina cardifolia, Dhaora Anogeissus latifolia, Salai Boswellia
serrata, Amla Emblica officinalis, Amaltas Cassia fistula,
and Gamhar Gmelina arborea (Singh 2014).
Field visits were carried out in
the morning (0600–1100 h) and in the afternoon (1500–1900 h), when birds were
found to be most active during December 2015 and February 2016. Various survey
methods like line transect (3 in each habitat, about 900–1,150 m long track)
and point transect (5 in each habitat) that were randomly placed, along with
opportunistic sightings were used to record various bird species of the region
(Bibby et al. 2000; Sutherland 2006). Olympus 10×50 DPSI binoculars and Canon
PowerShot sx500 IS camera were used for observation and photographs were taken
whenever it was possible. Identification and categorization of avian species
according to their migratory status either resident (R), winter visitor (WV),
or passage visitor (PM) was done using field guides (Kazmierczak & van
Perlo 2000; Grimmett et al. 2011). Bird species included in different IUCN Red
List categories (IUCN 2020) and Schedule under the Wildlife (Protection) Act,
1972 (BNHS 2002) were also taken into account while preparing the checklist.
Based on the frequency of observation, following categorizations were made:
Common (C): frequently observed in the study area (encountered during sampling
in more than 60% cases); Uncommon (UC): spotted on multiple occasions but not
as frequently as in case of common (encountered during sampling in more than
30% but less than 60% cases); Rare (R): not frequently encountered in the
entire study period (encountered during sampling in less than 30% cases).
Feeding habits (guilds) of birds were recorded as per observation and following
published literature (Ali & Ripley 1987).
Results
and Discussion
One-hundred-and-thirty-three bird
species belonging to 47 families and 13 orders were recorded during the study
period of which 123 were recorded from Site I and 112 were recorded from Site
II (Table 1). The highest number of bird species were recorded from
Accipitridae and Anatidae family (11 spp. each) followed by Turdinae (8 spp.)
and Ardeidae (7 spp.). The checklist of birds of the two districts is
represented in Table 1 while the number of bird species and their families is
graphically represented in Figure 2. According to the observed frequency, 37
bird species (27.82 %) were common, 79 species (59.40 %) were uncommon, and 17
species (12.78 %) were rare. Availability of diverse resources, habitat heterogeneity,
and different anthropogenic factors influences the avian diversity of the
studied sites. Avian species were categorized according to their migratory
status (either resident, winter visitor, or passage visitor). Ninety-three
species were resident, 39 species were winter visitors and only a single
species was passage visitor (Rosy Starling).
Habitat-wise avian richness
varied widely during the present study. Wetland (WL) harboured a maximum number
(69) of avian species, followed by agricultural land (AL, 56 spp.) and open
scrub jungle (OS, 50 spp.). These high numbers might indicate the ability of
certain bird species to occupy diverse habitat types. However, in grassland
(GL) and dry deciduous forest (DF) habitats, avian richness was quite low; 33 and
24 species were recorded from GL and DF habitats respectively (Figure 3).
Wetlands were an important habitat that sustains a substantial number of
waterbirds and wetland-associated birds (Kumar et al. 2005). However, most of
the small water bodies were temporary that eventually dried up in summer.
During winter, water was pumped out for irrigation by farmers of nearby
agricultural fields but still, the wetlands harboured rich avifauna.
Agricultural fields were also an important habitat that sustains the rich
diversity of avifauna in different landscapes (Hossain & Aditya 2014; Swamy
et al. 2015; Kumar & Sahu 2020). The present study also revealed the
importance of wetland and agricultural fields as avian habitats.
In the present study, we recorded
that 74 avian species (i.e., 55.64 % of total recorded spp.) were found
exclusively in a single habitat (Figure 4). Among this, highest number of
species (58 spp.) were exclusively recorded from WL habitat. Similar findings were also recorded by
Chatterjee et al. (2013) while working in sub-Himalayan forest patches.
Waterbirds were specialists in resource utilization (utilizing feeding habitat
and foraging technique selection) therefore they show strong fidelity towards
wetlands (Chatterjee et al. 2020). However, in other habitats, the number of
species that were solely found in that habitat was much less. In DF, AL, and OS
the number of species was seven, six, and three, respectively. In GL no such
species were recorded (Figure 3). The rest of the species are found in more
than one habitat. 31 species (23.31 %) were found in two habitats, 19 species
(14.29 %) in three habitats, seven species (5.26 %) in four habitats, and only
two species (1.50 %) were recorded from all five habitats (Figure 4).
A total of eight feeding habits
(guilds) were recorded including omnivorous (Om), phytophagous (Ph),
carnivorous (Cr), insectivorous (In), frugivorous (Fg), granivorous (Gr),
nectarivores (Nc), and scavengers (Sc). Few species had more than one feeding
habit and species feeding on diverse food items belonging to different trophic
levels were designated as Om. Om birds were most abundant (47 spp.) followed by
Cr (36 spp.), In (29 spp.), Gr (16 spp.), Ph (9 spp.), and Fg (5 spp.).
Foraging guilds dominated by Om birds were also recorded by several workers
like Yashmita-Ulman & Singh (2021), Noreen & Sultan (2022). The
increase in the abundance of Om birds is possibly due to a change in food
resources as a result of urbanization (Marzluff & Rodewald 2008). Two species,
recorded during the present study were scavengers (Sc) viz., Neophron
percnopterus (Egyptian Vulture), and Gyps bengalensis (White-rumped
Vulture). Scavengers play an important role in the ecosystem by feeding on
carcasses and/or human garbage (Moleón et al. 2014) and are much susceptible to
anthropogenic effects (Ogada et al. 2011). Once vultures were abundantly
distributed in this region as mentioned by the local inhabitants in and around
the study site, but during our study period, they were recorded only from Site
I and the encounter rate was rare (less than 5 individuals in the entire study
area) for both the species. The decline in the number of vultures may be
attributed to the use of diclofenac drugs, habitat destruction, food scarcity,
deforestation, and other reasons like power line collisions & natural
disasters (Jha et al. 2020). Cinnyris asiaticus Purple Sunbird was the
only Nc species observed during the present study (Figure 5). Site-wise
composition of avian species based on feeding habit was represented in Figure
6.
During our present study, we
recorded more than 400 individuals of Anser indicus Bar-headed Goose
(Image 2A) from a partially dried-up wetland. This species is assessed as Least
Concern (LC) according to the IUCN Red List. Though the population trend
appears to be declining (BirdLife International 2020b), based on the IUCN Red
List of threatened species (version 2020-1), Critically Endangered species like
Gyps bengalensis (White-rumped Vulture, Image 2B), Endangered species like Neophron
percnopterus (Egyptian Vulture, Image 2C), Vulnerable species like Aythya
ferina (Common Pochard), Antigone antigone (Sarus Crane), Lanius
meridionalis (Southern Grey Shrike, Image 2D) and Ciconia episcopus
(Woolly-necked Stork, Image 2E) were recorded during the present study. Near
Threatened bird species like Threskiornis melanocephalus (Black-headed
Ibis, Image 2F), Limosa limosa (Black-tailed Godwit, Image 2G), Esacus
recurvirostris (Great Thick-knee, Image 2H), Anhinga melanogaster
(Oriental Darter), Mycteria leucocephala (Painted Stork, Image 2I), Sterna
aurantia (River Tern, Image 2J) and Pelecanus philippensis
(Spot-billed Pelican, Image 2K) were also observed in the study area. Besides
11 avian species listed in Schedule I under the Wildlife (Protection) Act, 1972
were recorded during the present study. The majority of the globally threatened
species were recorded exclusively from wetlands. During wintering seasons these
water bodies were used for irrigation of agricultural fields. This water usage accelerates
the drying of small wetlands. To protect the waterbird diversity in this region
proper management policies should be taken. It is necessary to adopt
alternative irrigation schemes for farmers to conserve the wetland habitats.
This semi-arid landscape had
immense importance in the avian study. There were two Important Bird and
Biodiversity Areas (IBAs) situated within the present study area viz,
Gandhisagar Reservoir (IN-MP-06) and Sailana Kharmor Sanctuary (IN-MP-15). This
region especially, Sailana Kharmor Sanctuary is a native breeding ground of
endangered Lesser Florican Sypheotides indicus and many other species
(Rahmani et al. 2016). This region of the Indian subcontinent serves as a
terminus for avian species who migrate following the Central Asian/ South Asian
Flyway. These birds breed in the northern part of Russia (Siberia) in the east
to as far west as Europe covering parts of China, central and western Asia. Anser
indicus, the world’s highest-altitude migrant follow this route directly
over the Himalaya (BirdLife International 2020a) and congregate in different
wetlands of sub-Himalayan regions. The presence of a large non-breeding
wintering population of Anser indicus, never reported earlier
within the study site indicated the importance of conservation of wetland
habitats of this region.
The present study area is
situated within Biome 11 (i.e., Indo-Malayan tropical dry zone) and harboures
many biome-restricted birds. BirdLife International identified 59 such species
from this biome. We recorded several biome-restricted species which included Gyps
bengalensis (White rumped vulture), Butastur teesa (White-eyed
Buzzard), Pavo cristatus (Indian Peafowl), Vanellus malabaricus
(Yellow-wattled Lapwing), Psittacula cyanocephala (Plum-headed
Parakeet), Ocyceros birostris (Indian Grey Hornbill), Eremopterix
griseus (Ashy-crowned Sparrow-lark), Saxicoloides fulicata (Indian
Robin), Turdoides malcolmi (Large Grey Babbler), Turdoides striatus
(Jungle Babbler), Prinia socialis (Ashy Prinia) (Parveen &
Ilyas 2019).
The presence of significant
numbers of winter migrants, globally threatened species, biome–restricted
species amply supported that this semi-arid landscape was both ecologically and
biologically significant for breeding and migratory birds. However, presently avian populations in
semi-arid regions are declining rapidly due to unplanned developmental
activities, urbanization, and climate change (Khan et al. 2019). Therefore, it
is need of the hour to develop different conservation strategies like raising
awareness among local residents, community participation, long term monitoring,
and research, conservation of unique avian habitats, and restoration of
degraded habitats. Implementation of proper management policies both at the
central and state government levels with the involvement of different
stakeholders is necessary to protect the avian species and their habitats
outside the protected areas.
Table 1. Checklist of avifauna
recorded from semi-arid landscape of western Madhya Pradesh (Site I: Mandsaur
and Site II: Ratlam).
Scientific name |
Common name |
Migratory status |
IUCN Red List category |
WPA schedule |
Site I |
Site II |
Frequency of observation |
Habitat (s) |
Feeding habit |
Order: Galliformes |
|
|
|
|
|
|
|
|
|
Family: Phasianidae |
|
|
|
|
|
|
|
|
|
Pavo cristatus |
Indian Peafowl |
R |
LC |
I |
⁺ |
⁺ |
UC |
AL, OS |
Om |
Francolinus pondicerianus |
Grey Francolin |
R |
LC |
IV |
⁺ |
⁺ |
C |
GL, OS |
Om |
Francolinus pictus |
Painted Francolin |
R |
LC |
IV |
⁺ |
⁺ |
UC |
GL, OS |
Om |
Order: Anseriformes |
|
|
|
|
|
|
|
|
|
Family: Anatidae |
|
|
|
|
|
|
|
|
|
Anser indicus |
Bar-headed Goose |
WV |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Ph |
Anas crecca |
Common Teal |
WV |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Ph |
Nettapus coromandelianus |
Cotton Pygmy-Goose |
R |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Ph/Cr |
Tadorna ferruginea |
Ruddy Shelduck |
WV |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Om |
Aythya fuligula |
Tufted Duck |
WV |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Ph/Cr |
Anas acuta |
Northern Pintail |
WV |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Ph/Cr |
Anas clypeata |
Northern Shoveler |
WV |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Cr |
Anas poecilorhyncha |
Indian Spot-billed Duck |
R |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Ph/Cr |
Anser anser |
Greylag Goose |
WV |
LC |
IV |
⁺ |
⁺ |
R |
WL |
Ph |
Netta rufina |
Red-crested Pochard |
WV |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Ph/Cr |
Aythya ferina |
Common Pochard |
WV |
VU |
IV |
⁺ |
⁺ |
UC |
WL |
Ph/Cr |
Order: Piciformes |
|
|
|
|
|
|
|
|
|
Family: Picidae |
|
|
|
|
|
|
|
|
|
Dendrocopos mahrattensis |
Yellow-crowned Woodpecker |
R |
LC |
IV |
⁻ |
⁺ |
UC |
OS, DF |
In |
Order: Bucerotiformes |
|
|
|
|
|
|
|
|
|
Family: Bucerotidae |
|
|
|
|
|
|
|
|
|
Ocyceros birostris |
Indian Grey Hornbill |
R |
LC |
I |
⁺ |
⁺ |
UC |
DF |
Om |
Order: Upupiformes |
|
|
|
|
|
|
|
|
|
Family: Upupidae |
|
|
|
|
|
|
|
|
|
Upupa epops |
Common Hoopoe |
R |
LC |
NI |
⁺ |
⁺ |
UC |
AL |
In |
Order: Coraciiformes |
|
|
|
|
|
|
|
|
|
Family: Coraciidae |
|
|
|
|
|
|
|
|
|
Coracias benghalensis |
Indian Roller |
R |
LC |
IV |
⁺ |
⁺ |
C |
OS, AL |
Om |
Family: Alcedinidae |
|
|
|
|
|
|
|
|
|
Ceryle rudis |
Pied Kingfisher |
R |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Cr |
Halcyon smyrnensis |
White-throated Kingfisher |
R |
LC |
IV |
⁺ |
⁺ |
C |
WL |
Om |
Alcedo atthis |
Common Kingfisher |
R |
LC |
IV |
⁺ |
⁺ |
C |
WL |
Cr |
Family: Meropidae |
|
|
|
|
|
|
|
|
|
Merops orientalis |
Green Bee-eater |
R |
LC |
NI |
⁺ |
⁺ |
C |
OS, AL |
In |
Order: Cuculiformes |
|
|
|
|
|
|
|
|
|
Family: Cuculidae |
|
|
|
|
|
|
|
|
|
Eudynamys scolopaceus |
Asian Koel |
R |
LC |
IV |
⁺ |
⁺ |
C |
DF |
Om |
Order: Psittaciformes |
|
|
|
|
|
|
|
|
|
Family: Psittacidae |
|
|
|
|
|
|
|
|
|
Psittacula cyanocephala |
Plum-headed Parakeet |
R |
LC |
IV |
⁺ |
⁺ |
C |
AL, DF |
Fg |
Psittacula krameri |
Rose-ringed Parakeet |
R |
LC |
IV |
⁺ |
⁺ |
C |
AL, DF |
Fg |
Order: Strigiformes |
|
|
|
|
|
|
|
|
|
Family: Strigidae |
|
|
|
|
|
|
|
|
|
Athene brama |
Spotted Owlet |
R |
LC |
IV |
⁺ |
⁻ |
UC |
OS, AL, DF |
Cr |
Order: Columbiformes |
|
|
|
|
|
|
|
|
|
Family: Columbidae |
|
|
|
|
|
|
|
|
|
Columba livia |
Common Pigeon |
R |
LC |
IV |
⁺ |
⁺ |
C |
AL, DF, OS, WL, GL |
Gr |
Streptopelia decaocto |
Eurasian Collared-Dove |
R |
LC |
IV |
⁺ |
⁺ |
C |
AL, DF, OS, WL, GL |
Gr |
Spilopelia senegalensis |
Laughing Dove |
R |
LC |
IV |
⁺ |
⁺ |
C |
OS, AL, DF |
Gr |
Spilopelia chinensis |
Spotted Dove |
R |
LC |
IV |
⁺ |
⁺ |
C |
AL, DF, OS, GL |
Gr |
Order: Gruiformes |
|
|
|
|
|
|
|
|
|
Family: Gruidae |
|
|
|
|
|
|
|
|
|
Antigone antigone |
Sarus Crane |
R |
VU |
IV |
⁺ |
⁺ |
R |
AL |
Om |
Family: Rallidae |
|
|
|
|
|
|
|
|
|
Gallinula chloropus |
Common Moorhen |
R |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Om |
Porphyrio porphyrio |
Grey-headed Swamphen |
R |
LC |
IV |
⁻ |
⁺ |
UC |
WL |
Om |
Amaurornis phoenicurus |
White-breasted Waterhen |
R |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Om |
Fulica atra |
Eurasian Coot |
R |
LC |
IV |
⁺ |
⁺ |
C |
WL |
Om |
Order: Ciconiiformes |
|
|
|
|
|
|
|
|
|
Family: Pteroclididae |
|
|
|
|
|
|
|
|
|
Pterocles exustus |
Chestnut-bellied Sandgrouse |
R |
LC |
IV |
⁺ |
⁺ |
UC |
AL |
Gr |
Pterocles indicus |
Painted Sandgrouse |
R |
LC |
IV |
⁻ |
⁺ |
UC |
AL, OS |
Gr |
Family: Scolopacidae |
|
|
|
|
|
|
|
|
|
Gallinago gallinago |
Common Snipe |
WV |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Cr |
Limosa limosa |
Black-tailed Godwit |
WV |
NT |
IV |
⁺ |
⁺ |
UC |
WL |
Cr |
Tringa totanus |
Common Redshank |
WV |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Cr |
Actitis hypoleucos |
Common Sandpiper |
WV |
LC |
IV |
⁺ |
⁺ |
C |
WL |
Cr |
Tringa stagnatilis |
Marsh Sandpiper |
WV |
LC |
IV |
⁻ |
⁺ |
R |
WL |
Cr |
Calidris pugnax |
Ruff |
WV |
LC |
IV |
⁺ |
⁻ |
R |
WL |
Om |
Family: Jacanidae |
|
|
|
|
|
|
|
|
|
Metopidius indicus |
Bronze-winged Jacana |
R |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Om |
Family: Burhinidae |
|
|
|
|
|
|
|
|
|
Burhinus oedicnemus |
Eurasian Thick-knee |
R |
LC |
IV |
⁻ |
⁺ |
UC |
WL |
Cr |
Esacus recurvirostris |
Great Thick-knee |
R |
NT |
IV |
⁻ |
⁺ |
R |
WL |
Cr |
Family: Charadridae |
|
|
|
|
|
|
|
|
|
Charadrius dubius |
Little Ringed Plover |
R |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Cr |
Charadrius alexandrinus |
Kentish Plover |
WV |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Cr |
Vanellus malabaricus |
Yellow-wattled Lapwing |
R |
LC |
IV |
⁺ |
⁺ |
UC |
WL, AL |
Cr |
Vanellus indicus |
Red-wattled Lapwing |
R |
LC |
IV |
⁺ |
⁺ |
C |
WL, AL |
Cr |
Family: Recurvirostridae |
|
|
|
|
|
|
|
|
|
Himantopus himantopus |
Black-winged Stilt |
WV |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Cr |
Family: Glareolidae |
|
|
|
|
|
|
|
|
|
Cursorius coromandelicus |
Indian Courser |
R |
LC |
NI |
⁺ |
⁻ |
R |
AL |
In |
Family: Laridae |
|
|
|
|
|
|
|
|
|
Larus ridibundus |
Black-headed Gull |
WV |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Om |
Sterna aurantia |
River Tern |
WV |
NT |
IV |
⁺ |
⁺ |
UC |
WL |
Om |
Chlidonias hybrida |
Whiskered Tern |
WV |
LC |
IV |
⁺ |
⁻ |
R |
WL |
Om |
Family: Falconidae |
|
|
|
|
|
|
|
|
|
Falco tinnunculus |
Common Kestrel |
WV |
LC |
IV |
⁺ |
⁺ |
C |
OS, DF, GL, AL |
Om |
Family: Accipitridae |
|
|
|
|
|
|
|
|
|
Neophron percnopterus |
Egyptian Vulture |
R |
EN |
IV |
⁺ |
⁻ |
R |
OS, DF |
Sc |
Gyps bengalensis |
White-rumped Vulture |
R |
CR |
IV |
⁺ |
⁻ |
R |
DF |
Sc |
Milvus migrans |
Black Kite |
R |
LC |
I |
⁺ |
⁺ |
C |
AL, OS |
Om |
Elanus caeruleus |
Black-winged Kite |
R |
LC |
I |
⁺ |
⁺ |
C |
AL, OS |
Om |
Spilornis cheela |
Crested Serpent Eagle |
R |
LC |
I |
⁻ |
⁺ |
UC |
DF |
Cr |
Circaetus gallicus |
Short-toed Snake Eagle |
R |
LC |
I |
⁺ |
⁺ |
C |
AL, GL, DF, OS |
Cr |
Circus pygargus |
Montagu’s Harrier |
WV |
LC |
I |
⁺ |
⁺ |
UC |
OS, AL, WL, GL |
Om |
Accipiter badius |
Shikra |
R |
LC |
I |
⁺ |
⁺ |
UC |
AL, GL, DF, OS |
Cr |
Pernis ptilorhynchus |
Oriental Honey Buzzard |
R |
LC |
I |
⁺ |
⁺ |
UC |
DF |
In |
Butastur teesa |
White-eyed Buzzard |
R |
LC |
I |
⁺ |
⁻ |
UC |
AL, GL, OS |
Om |
Pandion haliaetus |
Osprey |
WV |
LC |
I |
⁺ |
⁺ |
UC |
WL |
Cr |
Family: Podicipedidae |
|
|
|
|
|
|
|
|
|
Tachybaptus ruficollis |
Little Grebe |
R |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Om |
Podiceps cristatus |
Great-crested Grebe |
WV |
LC |
IV |
⁺ |
⁺ |
R |
WL |
Om |
Family: Anhingidae |
|
|
|
|
|
|
|
|
|
Anhinga melanogaster |
Oriental Darter |
WV |
NT |
IV |
⁺ |
⁺ |
R |
WL |
Cr |
Family: Phalacrocoracidae |
|
|
|
|
|
|
|
|
|
Microcarbo niger |
Little Cormorant |
R |
LC |
IV |
⁺ |
⁺ |
C |
WL |
Cr |
Phalacrocorax carbo |
Great Cormorant |
R |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Cr |
Family: Ardeidae |
|
|
|
|
|
|
|
|
|
Ardea cinerea |
Grey Heron |
R |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Cr |
Egretta garzetta |
Little Egret |
R |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Om |
Bubulcus ibis |
Cattle Egret |
R |
LC |
IV |
⁺ |
⁺ |
C |
WL, AL |
Om |
Ardea alba |
Great Egret |
R |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Cr |
Ardea intermedia |
Intermediate Egret |
WV |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Cr |
Ardeola grayii |
Indian Pond Heron |
R |
LC |
IV |
⁺ |
⁺ |
C |
WL |
Om |
Nycticorax nycticorax |
Black-crowned Night Heron |
R |
LC |
IV |
⁺ |
⁻ |
UC |
WL |
Om |
Family: Threskiornithidae |
|
|
|
|
|
|
|
|
|
Threskiornis melanocephalus |
Black-headed Ibis |
R |
NT |
IV |
⁺ |
⁺ |
UC |
WL |
Om |
Plegadis falcinellus |
Glossy Ibis |
R |
LC |
IV |
⁺ |
⁻ |
UC |
WL |
Om |
Platalea leucorodia |
Eurasian Spoonbill |
R |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Om |
Family: Pelecanidae |
|
|
|
|
|
|
|
|
|
Pelecanus philippensis |
Spot-billed Pelican |
R |
NT |
IV |
⁺ |
⁻ |
R |
WL |
Cr |
Family: Ciconiidae |
|
|
|
|
|
|
|
|
|
Anastomus oscitans |
Asian Openbill |
R |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Om |
Ciconia nigra |
Black Stork |
WV |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Cr |
Mycteria leucocephala |
Painted Stork |
R |
NT |
IV |
⁺ |
⁺ |
UC |
WL |
Cr |
Ciconia episcopus |
Woolly-necked Stork |
R |
VU |
IV |
⁺ |
⁺ |
UC |
WL |
Cr |
Ciconia Ciconia |
White Stork |
WV |
LC |
IV |
⁺ |
⁻ |
R |
WL |
Om |
Order: Passeriformes |
|
|
|
|
|
|
|
|
|
Family: Laniidae |
|
|
|
|
|
|
|
|
|
Lanius vittatus |
Bay-backed Shrike |
R |
LC |
NI |
⁺ |
⁺ |
C |
OS |
In |
Lanius meridionalis |
Southern Grey Shrike |
R |
VU |
NI |
⁺ |
⁺ |
UC |
OS, AL |
Om |
Family: Dicruridae |
|
|
|
|
|
|
|
|
|
Dicrurus macrocercus |
Black Drongo |
R |
LC |
IV |
⁺ |
⁺ |
C |
GL, AL, OS |
Om |
Family: Corvidae |
|
|
|
|
|
|
|
|
|
Dendrocitta vagabunda |
Rufous Treepie |
R |
LC |
IV |
⁺ |
⁺ |
UC |
DF |
Om |
Corvus macrorhynchos |
Indian Jungle Crow |
R |
LC |
IV |
⁺ |
⁺ |
C |
OS, GL, WL |
Om |
Corvus splendens |
House Crow |
R |
LC |
V |
⁺ |
⁺ |
C |
AL, OS, WL, GL |
Om |
Family: Sturnidae |
|
|
|
|
|
|
|
|
|
Acridotheres tristis |
Common Myna |
R |
LC |
IV |
⁺ |
⁺ |
C |
AL, OS, GL |
Om |
Pastor roseus |
Rosy Starling |
PM |
LC |
IV |
⁺ |
⁺ |
UC |
AL, OS, GL |
Om |
Gracupica contra |
Asian Pied Starling |
R |
LC |
IV |
⁺ |
⁻ |
UC |
AL, OS, GL |
Om |
Family: Hirundinidae |
|
|
|
|
|
|
|
|
|
Ptyonoprogne concolor |
Dusky Crag Martin |
R |
LC |
NI |
⁺ |
⁻ |
UC |
AL |
In |
Hirundo rustica |
Barn Swallow |
WV |
LC |
NI |
⁺ |
⁺ |
UC |
WL, AL |
In |
Hirundo smithii |
Wire-tailed Swallow |
R |
LC |
NI |
⁺ |
⁺ |
UC |
WL, AL |
In |
Family: Campephagidae |
|
|
|
|
|
|
|
|
|
Pericrocotus ethologus |
Long-tailed Minivet |
R |
LC |
IV |
⁺ |
⁻ |
R |
DF |
In/Fg |
Family: Pycnonotidae |
|
|
|
|
|
|
|
|
|
Pycnonotus cafer |
Red-vented Bulbul |
R |
LC |
IV |
⁺ |
⁺ |
C |
OS, AL, DF, GL |
Fg |
Family: Timaliinae |
|
|
|
|
|
|
|
|
|
Chrysomma sinense |
Yellow-eyed Babbler |
R |
LC |
IV |
⁺ |
⁻ |
UC |
OS, AL |
Om |
Turdoides striata |
Jungle Babbler |
R |
LC |
IV |
⁺ |
⁻ |
UC |
OS, DF |
Om |
Argya malcolmi |
Large Grey Babbler |
R |
LC |
IV |
⁺ |
⁺ |
C |
AL, OS, GL |
Om |
Argya caudata |
Common Babbler |
R |
LC |
IV |
⁺ |
⁺ |
C |
AL, OS, GL |
Om |
Family: Sylviidae |
|
|
|
|
|
|
|
|
|
Prinia socialis |
Ashy Prinia |
R |
LC |
IV |
⁺ |
⁺ |
C |
AL, OS, GL |
In |
Prinia inornata |
Plain Prinia |
R |
LC |
IV |
⁺ |
⁺ |
C |
AL, OS, GL |
In |
Orthotomus sutorius |
Common Tailorbird |
R |
LC |
IV |
⁺ |
⁺ |
C |
AL, OS, GL, DF |
In |
Family: Alaudidae |
|
|
|
|
|
|
|
|
|
Eremopterix griseus |
Ashy-crowned Sparrow Lark |
R |
LC |
IV |
⁺ |
⁺ |
C |
AL, OS, GL |
Gr/In |
Galerida cristata |
Crested Lark |
R |
LC |
IV |
⁻ |
⁺ |
UC |
AL |
Gr/In |
Mirafra erythroptera |
Indian Bushlark |
R |
LC |
IV |
⁺ |
⁺ |
UC |
OS |
Gr/In |
Ammomanes phoenicurus |
Rufous-tailed Lark |
R |
LC |
IV |
⁺ |
⁺ |
UC |
AL, GL |
Gr/In |
Family: Nectariniidae |
|
|
|
|
|
|
|
|
|
Cinnyris asiaticus |
Purple Sunbird |
R |
LC |
IV |
⁺ |
⁺ |
UC |
OS, DF, AL |
Nc |
Family: Ploceidae |
|
|
|
|
|
|
|
|
|
Ploceus philippinus |
Baya Weaver |
R |
LC |
IV |
⁺ |
⁻ |
UC |
OS |
Gr |
Passer domesticus |
House Sparrow |
R |
LC |
IV |
⁺ |
⁺ |
C |
AL, GL |
Gr |
Gymnoris xanthocollis |
Chestnut-tailed Petronia |
R |
LC |
IV |
⁻ |
⁺ |
R |
AL, OS |
Gr |
Family: Estrildinae |
|
|
|
|
|
|
|
|
|
Euodice malabarica |
Indian Silverbill |
R |
LC |
IV |
⁺ |
⁺ |
UC |
AL, GL, OS |
Gr |
Family: Turdinae |
|
|
|
|
|
|
|
|
|
Monticola solitarius |
Blue Rock Thrush |
WV |
LC |
IV |
⁺ |
⁻ |
UC |
OS, AL |
In |
Saxicoloides fulicatus |
Indian Robin |
R |
LC |
IV |
⁺ |
⁺ |
C |
AL, OS |
In/Fg |
Copsychus saularis |
Oriental Magpie Robin |
R |
LC |
IV |
⁺ |
⁺ |
UC |
AL, OS, DF |
In |
Phoenicurus ochruros |
Black Redstart |
WV |
LC |
IV |
⁺ |
⁺ |
UC |
OS, GL |
In |
Saxicola torquata |
Common Stonechat |
WV |
LC |
IV |
⁺ |
⁺ |
C |
AL, GL, OS |
In |
Saxicola caprata |
Pied Bushchat |
WV |
LC |
IV |
⁺ |
⁺ |
UC |
AL, GL, OS |
In |
Oenanthe isabellina |
Isabelline Wheatear |
WV |
LC |
IV |
⁺ |
⁻ |
R |
AL, GL |
In |
Cyanecula svecica |
Bluethroat |
WV |
LC |
IV |
⁺ |
⁺ |
UC |
WL, GL |
In |
Family: Motacillidae |
|
|
|
|
|
|
|
|
|
Motacilla alba |
White Wagtail |
WV |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
In |
Motacilla maderaspatensis |
White-browed Wagtail |
R |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
Om |
Motacilla citreola |
Citrine Wagtail |
WV |
LC |
IV |
⁺ |
⁻ |
UC |
WL |
In |
Motacilla cinerea |
Grey Wagtail |
WV |
LC |
IV |
⁺ |
⁺ |
UC |
WL |
In |
Anthus rufulus |
Paddyfield Pipit |
R |
LC |
IV |
⁺ |
⁻ |
UC |
GL, AL |
In |
Family: Emberizidae |
|
|
|
|
|
|
|
|
|
Emberiza melanocephala |
Black-headed Bunting |
WV |
LC |
IV |
⁺ |
⁺ |
R |
AL, OS |
Gr |
Melophus lathami |
Crested Bunting |
R |
LC |
IV |
⁺ |
⁺ |
UC |
OS, GL |
Gr |
Migratory status: R—Resident |
WV—Winter visitor | PM—Passage migrant; IUCN Category: CR—Critically Endangered
| EN—Endangered | LC—Least Concern | NT—Near Threatened | VU—Vulnerable; WPA
Schedule: NI—bird species that are not included either in Schedule-I,
Schedule-IV or Schedule-V of the Wildlife (Protection) Act, 1972; Frequency of
observation: R—Rare | C—Common | UC—Uncommon; Habitat type: WL—Wetland |
GL—Grassland | OS—Open scrub jungle | AL—Agricultural land | DF—Dry deciduous
forest; Feeding habit: Om—omnivorous | Ph—phytophagous | Cr—carnivorous |
In—insectivorous | Fg—frugivorous | Gr—granivorous | Nc—nectarivores |
Sc—scavenger.
For figures &
images - - click here
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