Avian Richness Analysis of Wadaj Dam and Ghod River Basin, India
1
Department of Zoology,
Institute of Science,
Dr. Homi Bhabha State University,
Mumbai,
Maharashtra
India
Corresponding author Email: gdjalanag@gmail.com
DOI: http://dx.doi.org/10.12944/CWE.20.2.28
Copy the following to cite this article:
Punde S. B, Ghadi A. A, Kulkarni M. N. Avian Richness Analysis of Wadaj Dam and Ghod River Basin, India. Curr World Environ 2025;20(2). DOI:http://dx.doi.org/10.12944/CWE.20.2.28
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Punde S. B, Ghadi A. A, Kulkarni M. N. Avian Richness Analysis of Wadaj Dam and Ghod River Basin, India. Curr World Environ 2025;20(2).
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Article Publishing History
| Received: | 2025-03-20 |
|---|---|
| Accepted: | 2025-09-01 |
| Reviewed by: |
Izolda Matchutadze
|
| Second Review by: |
Tatyana Vitaliyevna
|
| Final Approval by: | Dr. Marta Fischer |
Introduction
According to earlier reports, avian biodiversity offers a wide range of indirect necessary services through natural ecosystems, significant direct economic advantages to humanity, and a significant role in regulating ecosystem function and stability.1-5 The earth's biodiversity is not evenly distributed and may have anything from five to over fifty million species. Anthropogenic activity encompasses many human-induced disturbances that can exert both immediate and prolonged effects on wildlife by altering behavior, physiology, and reproduction, thereby impacting biodiversity, as noted by Bharucha and Gogate.8 Anthropogenic activities diminish the sustainability of local populations by restricting food and breeding possibilities, compromising habitat suitability, and elevating regional extinction rates of animal species, as indicated by studies conducted by Bhale et al.5-7
Asia is regarded as one of the most biodiversity-rich continents; nonetheless, the surge in human population has negatively impacted the region's diversity, since the growing populace need food and shelter, leading to agricultural intensification, urbanization, industrialization, and pollution. According to Bharucha A. K.8 and Green A.J.,15 conservation planning cannot proceed until all species' populations in urbanized and peri-urban areas have been surveyed. India has more than 1300 bird species, accounting for over 13% of all bird species worldwide, according to Ali et al.,2 Dinesh, K. et al.,12 and Grimmett R. et al.16,17 Regrettably, India holds the third position among countries with the highest number of endangered and uncommon species, following Brazil and Indonesia.
Birds are crucial for ecosystem management and biodiversity since they serve as bioindicators of healthy ecosystems, regulate disease vectors, recycle biomass, and reduce disposable waste levels. The quantity of birds in an ecosystem indicates the environmental quality, pollution level, security, and availability of food and habitat, according to Harney et al.18 and Hoyer et al.19 Mangroves provide millions of people with food, clean water, raw resources, and resistance against rising sea levels and storms by connecting land and its inhabitants with the sea. According to Dandapat et al.11, 50% of the world's mangrove forests have been destroyed due to coastal alteration and clearing, and mangrove environments support a large portion of the world's tropical biodiversity. Wetlands are home to almost 40% of bird species and about 12% of other faunal species worldwide. According to many researchers,7-9,11,14 the numerous resident and passage migrant aquatic birds use the mangrove vegetation as a suitable habitat for foraging, roosting, and breeding.
Materials and Methods
About Study Area
The Wadaj Dam is situated near Parunde hamlet in the Junnar Taluka of Pune District. Maharashtra, India 19.1522992°N, 73.849129°E.
Methodology
Point Count
Points were selected at upstream and downstream of Wadaj Dam and Ghod Basin to observe, count and identify bird species with the help of binocular and camera. From February 2023 to December 2024, two-week intervals from 5:05 pm to 6:35 pm and from 7:05 am to 9:05 am were used to monitor both domestic and migratory birds. Surveys were carried out on the walkways close to the wetland areas.
A Nikon Coolpix, model B700 camera was utilized for photographic documentation. During the study, no bird specimens were collected; instead, photographic images, videos, and audio recordings were prepared as reference materials, as similarly done by previous researchers.9-11,14 The field guides "The Book of Indian Birds" (Salim Ali2), "Birds of the Indian Subcontinent" (Grimmett and Inskipp),16 along with an online bird database, were utilized for avian identification. The avifauna of the Wadaj Dam and its surrounding area was systematically documented, with regular field visits conducted, as done by Bhale et. al.7
Shannon-Weiner Index
Bird diversity, richness of species, additionally species evenness are assessed using the Simpson Index (Simpson, 1949) and the Shannon-Wiener Index1,13 as diversity indexes. The foundation of the Shannon-Wiener Index is the presumption that all species are represented in the sample and that individuals are selected at random from a sizable, independently distributed population. For assessing biodiversity across various ecosystems or habitats, this measure is frequently used Ahmad Zamir & Elliot.1,13 A measure of variation that accounts for both evenness and richness is Simpson's Diversity Index. It has proven to be a helpful tool for comprehending the biodiversity profile throughout the study area. Using this index, species diversity within each kind of habitat was measured using Hutchinson's (1970)1,13 methodology and computed using the formula.
The Shannon-Wiener Index H' is equal to - E(Pi - Ln Pi) (1).
Us = 1 / Ds, according to Simpson's Diversity Index (13)
Ds = E(Pi - (Ni - 1) / (N - 1) is the Simpson's Dominance Index, Pi = Ni/N is the relative abundance of species, There are a total of N unique individuals in the universe, where Ni is the number of people in each species.
Local Occurrence Status
Classifying the proportional abundance with incidence rate of kinds of birds included modifying the categorization criteria proposed by Bull (1974). Species recorded between 200 and 1,000 individuals per day were categorized as abundant, whereas species detected in quantities greater than 1,000 individuals per day were categorized as very abundant. Species with daily counts of 21 to 50 individuals were classified as common, and those with counts between 51 and 200 individuals as very common.
Birds recorded in daily numbers ranging from 7 to 20 individuals were categorized as fairly common, whereas species observed between 1 and 6 individuals per day were regarded as uncommon. Additionally, species documented in similarly low numbers (1 to 6 individuals) but only on a seasonal basis were considered rare. Finally, species with highly infrequent sightings were classified as very rare.
Results
The study documents the presence of 107 bird species across 17 orders and 47 families which includes information on the scientific and common names as well as the conservation status of the birds as previously reported by researchers.6,18-21 This represents the first record of such a diverse avifauna in the Junnar Taluka of Pune District, Maharashtra, highlighting the significant bird diversity at Wadaj Dam. The variety of bird species observed, with some either visiting or permanently residing in the area, may be attributed to the lack of anthropogenic disturbance and the abundant availability of avian food sources within and surrounding the dam. The majority of the recorded species fall under the "Least Concern" (LC) conservation category, with only a small number classified as"Vulnerable" (VU) (Table 1).
Table 1: Composition of avifauna of the Ecosystem Ghod river Basin
Sr. No. | Order | Family | Scientific Name | Status |
1 | 1. Passeriformes | 1. Paridae | Parus cinereus | LC |
2 | 2. Muscicapidae | Saxicola torquatus | LC | |
3 | Copsychus fulicatus | LC | ||
4 | Cyornis tickelliae | LC | ||
5 | Cyornis whitei | LC | ||
6 | Oenanthe fusca | LC | ||
7 | Copsychus saularis | LC | ||
8 | Copsychus malabaricus | LC | ||
9 | Ficedula superciliaris | LC | ||
10 | Cyornis rufigastra | LC | ||
11 | Saxicola caprata | LC | ||
12 | 3. Sturnidae | Pastor roseus | LC | |
13 | Acridotheres fuscus | LC | ||
14 | Acridotheres tristis | LC | ||
15 | Sturnia pagodarum | LC | ||
16 | Sturnnus roseus | LC | ||
17 | Gracupica contra | LC | ||
18 | 4. Pycnonotidae | Pycnonotus cafer | LC | |
19 | Hypsipetes guimarasensis | LC | ||
20 | Pycnonotus jocosus | LC | ||
21 | 5. Hirundinidae | Petrochelidon luvicola | LC | |
22 | Cecropis abyssinica | LC | ||
23 | Cecropis striolata | LC | ||
24 | 6. Estriladidae | Lonchura punctulata | LC | |
25 | Euodice malabarica | LC | ||
26 | 7. Ciconiidae | Ciconia episcopus | NT | |
27 | 8. Passeridae | Passer domesticus | LC | |
28 | Passer montanus | LC | ||
29 | Passer flavolus | LC | ||
31 | Cistothorus palustris | LC | ||
32 | 10. Zosteropidae | Zosterops palpebrosus | LC | |
33 | Zosterops ceylonensis | LC | ||
34 | 11. Corvidae | Corvus culminatus | LC | |
35 | Corvus macrorhynchos | LC | ||
36 | Corvus enca | LC | ||
37 | Dendrocitta vagabunda | LC | ||
38 | 12. Polceidae | Ploceus philippinus | LC | |
39 | Ploceus manyar | LC | ||
40 | 13. Monarchidae | Terpsiphone paradise | LC | |
41 | Hypothymis azurea | LC | ||
42 | 14. Nectariniidae | Cinnyris asiaticus | LC | |
43 | Leptocoma zeylonica | LC | ||
44 | Cinnyris lotenius | LC | ||
45 | Anthrepetes rhodolaemus | NT | ||
46 | 15.Thraupidae | Loriotus luctuosus | LC | |
47 | 16. Dicruridae | Dicrurus macrocercus | LC | |
48 | 17. Cisticolidae | Prinia crinigera | LC | |
49 | Prinia inornata | LC | ||
50 | Prinia hodgsonii | LC | ||
51 | Prinia sylvatica | LC | ||
52 | 18.Fringillidae | Crithagra flaviventris | LC | |
53 | 19. Alaudidae | Galerida deva | LC | |
54 | 20. Emberizidae | Emberzia melanocephala | LC | |
55 | Emberzia lathami | LC | ||
56 | Emberiza buchanani | LC | ||
57 | 21. Campephagidae | Pericrocotus erythropygius | LC | |
58 | Pericrocotus cinnamomeus | LC | ||
59 | 22. Leiothrichidae | Turdoides malcolmi | LC | |
60 | 23.Rhipiduridae | Rhipidura albicollis | ||
61 | 24. Timaliidae | Mixornis gularis | LC | |
62 | 25. Vangidae | Tephrodornis pondicerianus | LC | |
63 | 2. Coraciiformes | 26. Alcedinidae | Halcyon smyrnensis | LC |
64 | Ceyx azureus | LC | ||
65 | 27. Coraciidae | Coracias benghalensis | LC | |
66 | 28. Meropidae | Merops orientalis | LC | |
67 | 3. Suliformes | 29.Phalacrocoracidae | Microcarbo pygmaeus | LC |
68 | 4. Piciformes | 30. Megalaimidae | Psilopogon haemacephalus | LC |
69 | 31. Picidae | Dinopium benghalense | LC | |
70 | 5. Psittaciformes | 32. Psittaculidae | Psittacula cyanocephala | LC |
71 | Psittacula krameri | LC | ||
72 | Loriculus vernalis | LC | ||
73 | 6. Accipitriformes | 33. Accipitridae | Accipiter chilensis | LC |
74 | Haliastur indus | LC | ||
75 | Accipiter nisus | LC | ||
76 | Accipiter badius | LC | ||
77 | Circus aeruginosus | LC | ||
78 | 34. Pandionidae | Pandion haliaetus | LC | |
79 | 7. Ciconiiformes | 35. Ciconiidae | Ciconia episcopus | NT |
80 | Anastomus oscitans | LC | ||
81 | 8. Columbiformes | 36. Columbidae | Streptopelia turtur | VU |
82 | Patagioenas leucocephala | LC | ||
83 | Columba livia | LC | ||
84 | Spilopelia chinensis | LC | ||
85 | Spilopelia senegalensis | LC | ||
86 | 9. Gruiformes | 37. Rallidae | Porphyrio porphyria | LC |
87 | Amaurornis phoenicurus | LC | ||
88 | 10. Cuculiformes | 38. Cuculidae | Eudynamys scolopaceus | LC |
89 | Centropus sinensis | LC | ||
90 | 11. Pelecaniformes | 39. Ardeidae | Bubulcus ibis | LC |
91 | Ardea alba modesta | LC | ||
92 | Ardeola grayii | |||
93 | 40. Threskiornithidae | Pseudibis papillosa | LC | |
94 | 12. Anseriformes | 41. Anatidae | Tadorna ferruginae | LC |
95 | Anser domesticus | LC | ||
96 | Anser indicus | LC | ||
97 | 13. Charadriiformes | 42. Charadriidae | Vanellus indicus | LC |
98 | Charadrius dubius | LC | ||
99 | Charadrius alexandrines | LC | ||
100 | 43. Recurvirostridae | Himantopus himantopus | LC | |
101 | 14. Galliformes | 44. Phasianidae | Pavo cristatus | LC |
102 | 15. Strigiformes | 45. Strigidae | Asio flammeus | LC |
103 | Bubo bubo | LC | ||
104 | Bubo bengalensis | LC | ||
105 | 16. Bucerotiformes | 46. Upupidae | Upupa epops | LC |
106 | 17. Falconiformes | 47. Falconidae | Falco tinnunculus | LC |
107 | Falco chicquera | NT |
Species richness was n = 159 in 2023 and n = 151 in 2024, whereas evenness of bird species compares the similarity of each species' population size recorded in February 2023 to December 2024, which was 0.31 and 0.30, respectively. The projected values of the Shannon-Weiner diversity index1,13 for the avifauna encountered in 2023 and 2024 were 3.09 and 3.00, respectively. A measure of variation that accounts for both evenness and richness is Simpson's Diversity Index. It has proven to be a helpful tool for comprehending the biodiversity profile throughout the study area. In 2023 and 2024, the anticipated Simpson's Diversity Index value for avi-fauna encountered was 0.745. Bird densities in 2023 and 2024 were 4.9 and 4.7 birds per hectare, respectively.
Discussion
In and around Wadaj Dam, 47 families and 17 orders of birds totaling 107 species were found throughout the investigation. Out of 107 species, 62 belong to Passeriformes, 04 to Coraciiformes, 01 to Suliiformes, 02 to Piciformes 03 to Psittaciformes, 05 to Accipitriformes, 02 to Ciconiiformes, 06 to Columbiformes, 02 to Gruiformes, 02 to Cuculiformes, 04 to Pelecaniformes 03 to Anseriformes, 04 to Charadiformes, 01 to Galliformes, 03 to strigiformes, 01 to Bucerotiformes and 02 to Falconiformes order. In present study 102 species are least concern, 4 species are Near Threatened, 1 species is Vulnerable. With 107 species from 17 orders and 47 families—of which Passeriformes make up the majority with 62 species—the current study demonstrates the remarkable bird diversity in and around Wadaj Dam.
This high species richness can be attributed to the ecological diversity of the Wadaj Dam and the Ghod Basin, which provide perennial water sources, varied microhabitats, and abundant food resources. Similar findings have been reported by Grimmett et al.16 and Ali & Ripley,2 who observed that wetlands surrounded by agricultural and semi-natural habitats often support a high diversity of avifauna due to their role as feeding, roosting, and breeding grounds.
The majority of the species (102) that have been documented are categorized as Least Concern, while four species are considered to be in danger of extinction along with one that is listed as Vulnerable (Prone to) on the IUCN Red List. This composition indicates a relatively healthy avian community, yet the presence of Near Threatened and Vulnerable species underscores the importance of continuous monitoring and targeted conservation strategies, as emphasized by BirdLife International.10 However, anthropogenic pressures such as hunting, trapping, and habitat disturbance remain significant threats in the region. Hunting of waterbirds, mammals, and reptiles for meat, coupled with the killing of birds perceived as agricultural pests, mirrors trends reported in other parts of India by Mukherjee et al.25 and Sundar & Subramanya.27 These practices, driven by cultural preferences and economic factors, have the potential to cause localized population declines.
The study reaffirms earlier conclusions by Lad et al.,24 and Kumar et al.,21 that comprehensive biodiversity surveys are essential for designing effective conservation programs. Community-based conservation approaches, particularly awareness campaigns, can reduce hunting pressure and promote coexistence between humans and wildlife. Furthermore, the development of ecotourism initiatives could provide alternative livelihoods, enhancing local economic well-being while incentivizing biodiversity protection, as suggested by Goodwin14 and Bhalla et al.9
Wadaj Dam and the Ghod Basin provide a continuous water supply throughout the year, fostering and flourishing the biodiversity in the region. However, hunting and a lack of awareness are significant threats to the biodiversity in this area. The region is unique in its ecological diversity and habitat, offering both feeding and breeding grounds for numerous organisms. The presence of agricultural land provides feeding opportunities for many bird species, some of which are considered pests by farmers and are often killed or harmed as investigated by Lad et al.24 Certain aquatic birds, mammals, and reptiles are hunted for their meat, which is considered a delicacy by the local population. Traps are set both for hunting purposes and to protect agricultural crops. As previously concluded the extensive study of the biodiversity in any study is crucial to support future conservation efforts.5,6,16,17,19, 23 Raising awareness among local communities will likely encourage their participation in conservation activities and could also offer them economic opportunities through the development of ecotourism.
Conclusions
The study area supports a rich avian diversity, according to the observations and data collected from the Wadaj Dam area, located near Parunde village in Junnar Taluka, Pune District, Maharashtra, India. Maximum bird diversity was recorded during the winter season, and the study area serves as both a feeding and breeding ground for numerous bird species. However, anthropogenic activities pose a significant threat to the existing avian diversity by destroying their breeding and feeding grounds. A strategic plan for the sustainable development of breeding and feeding grounds for avian diversity is needed to protect their habitats and preserve the unique biodiversity of the study area.
Acknowledgement
Authors are grateful to the Director and Head department of Zoology for their constant support during the research.
Funding Sources
The author (s) received no financial support for the research, authorship, and/or publication of this article.
Conflict of Interest
The authors do not have any conflict of interest.
Data Availability Statement
This statement does not apply to this article.
Ethics Statement
This research did not involve human participants, animal subjects. Or any material that requires ethical approval.
Informed Consent Statement
This study did not involve human participants, and therefore, informed consent was not required.
Permission to reproduce material from other sources
Not Applicable
Author Contributions:
Snehal Punde – Data Collection, Analysis, Writing – Review
Aparna Ghadi – Conceptualization, Methodology and Editing
Manisha Kulkarni – Funding Acquisition, Resource and Supervision
References
- Ahmad Z, Zamir M, Khan A, Iqbal S. Calculation of avian biodiversity through Shannon Weinner diversity index and Simpson diversity index. Int J Adv Res Eng Sci Manag. 2021;9(12).
- Ali S, Ripley SD. Handbook of Birds of India and Pakistan. Delhi: Oxford University Press; 1983:110-112.
- Ali S, Ripley SD. Compact Edition of the Handbook of the Birds of India and Pakistan. New Delhi: Oxford University Press; 1987.
- Allen D, Anderton J, Kazmierczak K. Report on an ornithological visit to Buxa Tiger Reserve, West Bengal, India, 17 February to 6 March 1992. Forktail. 1996;12:47-64.
- Anonymous. Wetland values and functions. Gland, Switzerland: The Ramsar Bureau; 2000:20-25.
- Bang P, Dahlstrom P. Collins Guide to Animal Tracks and Signs. London: Wm. Collins Sons and Co. Ltd.; 1980.
- Bhale P, Gupta RK, Krishnan MS. A Revised Survey of Forest Types of India. New Delhi: Government of India; 1968.
- Bharucha EK, Gogate PP. Avian profile of a man-modified aquatic ecosystem in the backwaters of Ujani Dam. J Bombay Nat Hist Soc. 1990;87(1):73-90.
- Bhalla RS, Weaver LC, Chhatre A. Ecotourism for community benefits: A case study from India. J Ecotourism. 2013;12(1):1-18.
- BirdLife International. IUCN Red List for birds. 2024. Accessed September 6, 2025. http://www.birdlife.org
- Dandapat A, Banerjee D, Chakraborty D. The case study of the disappearing House Sparrow (Passer domesticus indicus). Vet World. 2010;3(2):97-100.
- Dinesh KP, Radhakrishnan C, Gururaja KV, Deuti K, Bhatta G. A checklist of amphibia of India with IUCN Red List status. Updated April 2013. Zool Surv India. 2013.
- Tramer EJ. Bird species diversity: Components of Shannon’s formula. Ecology. 1969;50(5):927-932.
CrossRef - Goodwin H. Local community involvement in tourism around national parks: Opportunities and constraints. Curr Issues Tour. 2002;5(3):338-360.
CrossRef - Green AJ. Seasonal of globally threatened Anatidae in relation to threats, distribution, migration patterns and habitat use. Conserv Biol. 1996;10:1435-1445.
CrossRef - Grimmett R, Inskipp C, Inskipp T. Pocket Guide to the Birds of the Indian Subcontinent. Oxford: Oxford University Press; 2001.
- Grimmett R, Inskipp C, Inskipp T. Birds of the Indian Subcontinent. Oxford: Oxford University Press; 1998. 888 p.
- Harney NV, Dhamani AA, Andrew RJ. Avifaunal diversity in and around Kanhalalake near Bhadrawati, Dist Chandrapur (MS), India. Bionano Frontier. 2012;5(2-I):30-33.
- Hoyer MV, Canfield DE. Limnological factors influencing bird abundance and species richness on Florida lakes. Lake Reserv Manage. 1990;6:133-141.
CrossRef - Kulkarni AN, Kanwate VS, Deshpande VD. Birds in and around Nanded city, Maharashtra. Zoos Print J. 2005;20(11):2076-2078.
CrossRef - Kumar P, Singh R, Sharma A, Verma S. Avian diversity and conservation in Indian wetlands. Wetl Ecol Manag. 2019;27:1-15.
- Kurhade SM. Diversity of avifauna in Harishchandragad, Kalasubai area, Tal. Akole, Dist. Ahmednagar, Maharashtra. Newsl Birdwatchers. 2010;50(2):17-20.
- Lad D, Patil S. Status and diversity of avian fauna in the estuarine wetland area of Bhayander and Naigaon, Maharashtra, India. Biosci Discov. 2015;6(1):39-44.
- Lad R, Pawar P, Deshmukh V, Bhosale S. Human-bird conflict in agricultural landscapes. Indian J Ecol. 2018;45(2):243-249.
- Mukherjee A, Borad CK, Parasharya BM. Avifaunal profile of the wetlands of Gujarat, India. Zoos Print J. 2002;17(5):795-802.
CrossRef - Puri SD. Avifaunal diversity of Malguzari Lake at Zaliya near Amgaon in Gondia district (MS), India. Int J Life Sci. 2015;3(3):219-224.
- Sundar KSG, Subramanya S. Bird use of rice fields in the Indian subcontinent. Waterbirds. 2010;33 (1):44-70.
CrossRef


