Journal of Threatened Taxa | www.threatenedtaxa.org | 26 August 2023 | 15(8): 23742–23749

 

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

https://doi.org/10.11609/jott.8390.15.8.23742-23749

#8390 | Received 03 February 2023 | Final received 18 July 2023 | Finally accepted 08 August 2023

 

 

Notes on nesting behavior of Yellow-footed Green Pigeon Treron phoenicopterus (Latham, 1790) in Aligarh Muslim University campus and its surroundings, Uttar Pradesh, India

 

Ayesha Mohammad Maslehuddin 1 & Satish Kumar 2

 

1,2 Department of Wildlife Sciences, Aligarh Muslim University, Aligarh, Uttar Pradesh 202002, India.

1 ayesha.wildlife@gmail.com, 2 satishkumar.amu@gmail.com (corresponding author)

 

 

Editor: Anonymity requested.            Date of publication: 26 August 2023 (online & print)

 

Citation: Maslehuddin, A.M. & S. Kumar (2023). Notes on nesting behavior of Yellow-footed Green Pigeon Treron phoenicopterus (Latham, 1790) in Aligarh Muslim University campus and its surroundings, Uttar Pradesh, India. Journal of Threatened Taxa 15(8): 23742–23749. https://doi.org/10.11609/jott.8390.15.8.23742-23749

  

Copyright: © Maslehuddin & Kumar 2023. 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: The first author was awarded Junior Research Fellowship and subsequently Senior Research Fellowship by the University Grants Commission to conduct research.

 

Competing interests: The authors declare no competing interests.

 

Author details: Ayesha Mohammad Maslehuddin is a PhD candidate (UGC-NET SRF) at the Department of Wildlife Sciences, Aligarh Muslim University, Aligarh with keen interest in avian ecology and bioacoustics. Satish Kumar is presently an associate professor at the Department of Wildlife Sciences, Aligarh Muslim University, Aligarh. He has more than 25 years of research experience with specialization in wildlife ecology and management. He has been working on ecology of large carnivores, long-term monitoring of semi-arid ecosystems, avian ecology and behavior, conservation and management of threatened biodiversity.

 

Author contributions: AMM undertook field surveys, noted behavioral data, took images in the field, collected the literature for manuscript preparation and wrote the manuscript. SK designed and planned the study including interpretation of the data. SK checked the manuscript and provided inputs for improvements.

 

Acknowledgements: First author acknowledge Uttam, Amber, and Arif for their constant support and encouragement. Also, all help extended by Uttam during fieldwork is highly recognized and appreciated.

 

 

Abstract: The nesting behavior of the Yellow-footed Green Pigeon Treron phoenicopterus was observed during its breeding season in 2021 in an urban region encompassing the Aligarh Muslim University Campus and the surrounding areas. Data were collected by searching nests in the study area. The breeding season for the species in the study sites begins in March and re-nesting is attempted even in July. A total of 31 nests were found on 24 trees belonging to eight species. The analysis of nest site characteristics revealed that Millingtonia hortensis, Azadirachta indica, and Dalbergia sissoo were the most important nest tree species, accounting for 69% of the identified nests during the study period. These findings contribute to our understanding of the nesting behavior of the Yellow-footed Green Pigeon in an urban environment and have implications for its conservation and management.

 

Keywords: Aligarh Fort, canopy, columbidae, incubation, mating season, nest site characteristics, squabs, urban region.

 

 

INTRODUCTION

 

The Columbidae family is one of the world’s most threatened families. Despite its widespread distribution, the family, which contains pigeons and doves worldwide has received little conservation attention; is considered to have 369 species, 16 of whom are extinct, and one is extinct in the wild (the Socorro Dove Zenaida graysoni) (Birdlife International 2020). Thirty-three species of Columbidae have a distribution in India. It is most likely because it is one of a group of birds threatened by human persecution, habitat degradation, and introduced predators (Owens & Bennett 2000).

India has an incredible diversity of Columbiformes, inhabiting 33 species, including fruit pigeons (Ali & Ripley 1987; Grimmett et al. 2016). Frugivorous birds are the key functional species, performing valuable seed dispersal services and regeneration and their decline or local extinction may have severe consequences for the functioning of an ecosystem (McConkey & Drake 2002). Yellow-footed Green Pigeon is frugivorous species and is a common resident species in Aligarh district in Uttar Pradesh, where no studies have been carried out on its status, distribution, or ecology. As a result, we planned to investigate the Yellow-footed Green Pigeon nesting ecology in this area. It breeds in the Aligarh Muslim University campus and adjoining areas regularly, and the Indian Jungle Crow Corvus macrorhynchos and House Crow Corvus splendens prey on their clutches and nestlings. A few studies on Columbidae are by Bhattacharya (1994) on morphological adaptations, Somasundaram (2006) and Devi (2012) on the ecology of Nilgiri Wood Pigeon and Yellow-footed Green Pigeon, respectively, and Kour (2016) on eco-biology of some species from Jammu. Therefore, the present study was conducted to present preliminary data on the nesting behavior of Yellow-footed Green Pigeons in an urban region.

 

Study Area

Aligarh Muslim University is in Aligarh district in Uttar Pradesh, India, in the Ganga-Yamuna doab region. It is located at the northernmost part of the Agra division, stretching from 27.48330N to 28.01660N latitude and 77.48330E to 78.66660E longitude  (Image 1). The district covers an area of 3,650 km2 and is 130 km from Delhi. The flora in the area is dry deciduous with mostly deciduous trees in most areas. The locations of the nest and random plots at both the study sites, i.e., AMU campus (NCi & RCi) and Aligarh Fort (NQi & RQi) are shown in Image 2.

The study area has arid open scrub called ‘Rakhs’ (Champion & Seth 1968). The study region has soil known as ‘usar’, mesquite plantation, and agricultural terrain. Prosopis juliflora (a weed species from central America) dominates most forest patches, followed by Acacia catechu, P. cineraria, P. specigera, Melia azadirach, Azadirachta indica, Cordia dichotoma, Pongamia pinnata, Syzygium cumini, Dalbergia sissoo, Butea monosperma, Acacia nilotica, Acacia leucophloea, and Phoenix sylvestris (Yasmin 1995).

In central Ganga Plain, the interfluvial stretch of the Ganga and Yamuna passes through Aligarh district. Most of the principal physiographic are made out of alluvial infill. The deposition of the Ganga and Yamuna rivers significantly influences the main soil types in the district. The Aligarh Fort and AMU Campus in Aligarh city (27.91350N, 78.07820E) harbor a diverse range of flora, including exotic species that have been intentionally planted. The Aligarh Fort, now managed by the Aligarh Muslim University, serves as a botanical garden and spans over an area of 47.87 ha with an average elevation of around 200 m. The vegetation within the Fort can be classified into different types. The central plain area, covering 10.31 ha, predominantly consists of ornamental and fruit trees such as Terminalia arjuna, Mangifera indica, Psidium guajava, Emblica officinalis, Syzigium cuminii, Morus alba, Tectona grandis, Bombax ceiba, and others. Surrounding this central plantation is an elevated ridge of scrubland with eight bastions, covering 6.85 ha, featuring natural vegetation including Azadirachra indica, Dalbergia sissoo, and a dominant shrub cover of Capparis sepiaria. Prosopis juliflora is notably prominent in the ridge area of the Fort. Encircling the ridge is a 50-m-wide depression that consists of barren land, covering an area of 12.1 ha. During the monsoon season, this area is adorned with herbaceous plants, while dry seeds of these monsoon herbs are available for the rest of the year. The flora of the Fort includes various plants including shrubs, climbers, and trees. Additionally, the area is inhabited by several mammalian species, including the Indian Grey Mongoose Herpestes edwardsii, Jungle Cat Felis chaus, Indian Hare Lepus nigricollis, Indian Gerbil Tatera indica, Five-striped Palm Squirrel Funambulus pennantii, India Bush Rat Golunda ellioti, and Rhesus Monkey Macaca mulatta, as documented in previous studies (Qureshi 1991; Khan 1992; Khan 2014).

 

 

METHODS

 

Based on Devi (2012), the study focused on observing the nesting behavior of the Yellow-footed Green Pigeon during its 2021 breeding season in an urban region. The study sites included the Aligarh Muslim University (AMU) campus, Naqvi Park (27.9022° N, 78.0733° E), and the Aligarh Fort (27.9135° N, 78.0707° E). The methodology adopted by Devi (2012) aimed to understand the characteristics of the nesting sites and the factors influencing nesting site selection. To quantify the nesting environment, the methods outlined by James & Shugart (1970), subsequently refined by Mudappa & Kannan (1997), were employed. Data on nesting trees and nesting environment factors were collected and quantified. In order to detect nests of Yellow-footed Green Pigeons in the beginning of their nesting season, we largely depended on their behavioral cues such as collecting nesting material. During the mating season of Yellow-footed Green Pigeons, nest searches were conducted in the study region, and observations on nest trees and nest-site characteristics were made, following the methods used in previous studies (Gokula 2001; Devi & Saikia 2012). To ensure minimal disturbance to the nesting birds, all observations of their nesting activities were conducted from a safe distance, thus preserving the natural nesting behavior of the Yellow-footed Green Pigeon.

Observations of its nesting sites and nest site characteristics were undertaken from 10 March to 13 July 2021, when the final fledglings of active nests fledged. Once an individual or pair was sighted gathering twigs from the trees or constructing a nest, they were followed using binoculars or a camera and their nesting activities were recorded daily from 0630 h to 1130 h. A comprehensive dataset was obtained by closely observing selected nests, while additional nests were also monitored to determine the overall nesting success and gather supplementary data.

Adult birds undertaking breeding activities such as nest construction, incubation, and feeding the young in or near the nest indicated the presence of an active nest. A circular plot with a radius of 10 m was set up around each nesting tree to measure nest-site selection along with random plots which were also placed at a distance of 30–50 m from the nest plot. All characteristics were recorded in these plots as exercised in some earlier investigations (James & Shugart 1970; MacKenzie & Saely 1981; Clark et al. 1983; Sieg & Becker 1990; Liebezeit & George 2002).

Nest site and random site characteristics recorded during the study were tree number to be used subsequently for density calculations (trees/hectare), tree height (m), tree GBH (cm), basal area (m2), the height of the first branch (m), distance from the nearest road (m), distance from nearest habitation (m), ground cover (%), shrub cover (%), canopy cover (%), canopy spread (m3) and nest height (m). In addition, the species of nesting trees were identified and recorded. To ensure comparability and permit statistical analysis, the collected data were normalized beforehand. In the Qila (Aligarh Fort) area, the listed nest plots were labeled as NQi, while the random plots were labeled as RQi. On the other hand, in the University Campus area, the nest plots were labeled as NCi, and the random plots as RCi.

 

 

RESULTS

 

The Yellow-footed Green Pigeon’s mating season begins in March and continues until July having re-nesting attempts towards the end of June and July. During this period, birds whose nests have been destroyed by predators seek to re-nest (Ayesha Mohammad Maslehuddin pers. obs. 31 May 2021). A total of thirty-one nests of Yellow-footed Green Pigeons were found, with 14 nests located at Aligarh Fort and 12 nests situated on the AMU campus. These nests were distributed among 26 trees in the study area. Out of the 26 nest trees, six were Prosopis juliflora (25%), five Azadirachta indica (Neem) (21%), four Millingtonia hortensis (Indian Cork Tree), and Dalbergia sissoo (Sheesham) (17%), two were Mangifera indica (Mango) and one each of Holoptelea integrifolia (Jungle Cork Tree), Syzygium cumini (Black Plum), and Bombax ceiba (Silk Cotton Tree) (Table 1).

The GBH of non-nest trees (0.46 ± 0.03) was slightly higher than that of the nest trees (0.42 ± 0.05) (Figure 1), but there was no significant difference (t = -0.754, p >0.05) among them.

The canopy cover of non-nest trees (63.35 ± 2.26) was greater than the canopy cover of nest trees (58.37 ± 4.36) (Figure 2), and the difference was significant (t = 17.958, p <0.05).

Tree species used for nesting by Yellow-footed Green Pigeons were Millingtonia hortensis, Prosopis juliflora, Azadirachta indica, Dalbergia sisso, Holoptelea integrifolia, Mangifera indica, Syzygium cumini, and Bombax ceiba. The number of nests on different tree species and the total number of individuals of each species, including those in the centre of random plots, are shown in Figure 3. The maximum number of nests were found on Millingtonia hortensis.

 

 

DISCUSSION AND CONCLUSION

 

The semi-natural plantations on the AMU Campus provide habitat to a wide variety of avifaunal species. The current study was one of the few attempts to acquire useful data regarding the ecology of species nesting.

Nest site characteristics show that Millingtonia hortensis, Azadirachta indica, and Dalbergia sissoo are essential nest tree species accounting for 69% of the total nest trees identified during the study period. These tree species ranged 11–25 m in height and were branched and bifurcated to provide a better place to hold the nest and a safe base for the pigeons to make their nests. Another reason was the abundance of these tree species at the study site.

The study revealed that the breeding season of Yellow-footed Green Pigeon is from late March to July in the study area. Nest building begins in early April, and they make open nests of mostly twigs (Image 3). Nests of Yellow-footed Green Pigeons are very simple in structure and made up of small twigs placed crisscrossed over one another. Both sexes were seen sharing nest building and duty of incubation, i.e., one of the breeding males or females continued to sit on the eggs while the other pair went foraging. As per observation, only one squab is hatched per nest. The duration from nest building until the fledgling left the nest was 39–44 days.

Nest building by Yellow-footed Green Pigeons was observed during the study period. Most of the nest-building activity occurred 0630–1000 h. Nest materials such as twigs were collected from dried branches of Holoptelea integrifolia, Azadirachta indica, Tectona grandis, Eucalyptus citriodora, Syzygium cumini, and Casuarina equisetifolia trees 15–30 m away from nest site by one of the mates. One of the breeding pair individuals broke suitable twigs from the branches and carried them toward the nest. The waiting individual on the tree gently arranged it into the nest securely. Also, it was observed that the individual carrying the twig never landed directly at the location where another mate was building the nest; instead, it would land on branches higher in the canopy and then move down towards the nest location cautiously. Apart from these, the frequency of nest-building trips was maximum during the 2nd and 3rd days of nesting, which gradually declined in the following days.

During the study, birds of prey such as Pariah Kites Milvus migrans and occasionally crows (Corvus splendens or C. macrorhynchos) were commonly seen preying on nests of Yellow-footed Green Pigeon. Some competitors like Common Mynas Acridotheres tristis, Eurasian Collared Dove Streptopelia decaocto, and Indian Palm Squirrel Funambulus palmarum mostly destroyed the nests; they forcefully entered the nest area of the pigeon, destroyed it and occupied the territory. Natural calamities like heavy rain and the storm destroyed most nests during the pre-hatching stage. Generally, the Yellow-footed Green Pigeons construct their nests on softwood trees, which are easily broken due to heavy rain and storm.

Association of yellow-footed Green Pigeons with the Black Drongo Dicrurus macrocercus during nesting season (Image 3) may be a great driver in predicting nests’ success and subsequently emerging chicks. Around 40% of nests were successfully raised due to a Black Drongo nest in the vicinity of nests of Yellow-footed Green Pigeons. It has also been observed by Ali & Ripley (1987).

The success of nesting attempts by Yellow-footed Green Pigeons was determined based on the presence of hatched squabs in each nest. Of all the nests encountered, it was determined that only 35% achieved successful nesting, indicating the successful hatching of squabs. In contrast, the remaining 65% of nests were deemed unsuccessful due to their destruction by storms or abandonment caused by excessive disturbance, resulting in the absence of hatched squabs.

 

Table 1. Characteristics of nest tree species of Yellow-footed Green Pigeon in the study area.

 

Tree species

Tree height (m)

Tree GBH (m)

Wood type

Foliage type

No. of nests

1

Millingtonia hortensis

15–25

0.20–0.55

Softwood

Deciduous

9

2

Azadirachta indica

10–21

0.19–1.09

Softwood

Deciduous

5

3

Dalbergia sisso

10–15

1.20–1.40

Hardwood

Deciduous

4

4

Prosopis juliflora

10–17

0.20–0.65

Softwood

Deciduous

6

5

Holoptelea integrifolia

17–27

0.22–1.11

Softwood

Deciduous

3

6

Mangifera indica

15–21

0.36–0.85

Softwood

Deciduous

2

7

Syzygium cumini

17–21

0.57–0.67

Softwood

Deciduous

1

8

Bombax ceiba

18–20

0.25–0.71

Softwood

Deciduous

1

 

 

For figures & images - - click here for full PDF

 

REFERENCES

 

Ali, S. & S.D. Ripley (1987). Handbook of the Birds of India and Pakistan. Compact edition, Oxford University Press, New Delhi, 737 pp.

Birdlife International (2020). Species factsheet: Zenaida graysoni. Downloaded from http://www.birdlife.org on 14 September 2021.

Bhattacharya, B.N. (1994). Diversity of feeding adaptations in certain columbid birds:  a functional morphological approach. Journal of Bioscience 19(4): 415–427.

Champion, H.G. & S.K. Seth (1968). A Revised Survey of The Forest Type of India. Govt. of India Press. New Delhi, 404 pp.

Chapman, C.A. & L.J. Chapman (1995). Survival without dispersers: seedling recruitment under parents. Conservation Biology 9(3): 675–678.

Clark, L., R.E. Ricklefs & R.W. Schreiber (1983). Nest-site selection by the Red-tailed Tropicbird. The Auk 100(4): 953–959.

Devi, O.S. (2012). Diversity of Frugivorous birds and Ecology of Brown Hornbill Anorrhinus tickelli (Blyth) and Yellow-legged Green-pigeon Treron phoenicoptera (Latham) in Jeypore Reserve Forest, Assam. PhD Thesis. Department of Zoology, Guwahati University, 184 pp.

Devi, O.S. & P.K. Saikia (2012). Nest-site characteristics of Yellow-legged Green- Pigeon, Treron phoenicoptera in a tropical evergreen forest patches of eastern Assam, India. The Bioscan 7(2): 277–282.

Gokula, V. (2001). Nesting ecology of the Spotted Munia Lonchura punctulata in Mudumalai Wildlife Sanctuary (Southern India). Acta Ornithologica 36(1): 1–5.

Grimmett, R., C. Inskipp & T. Inskipp (2016). Birds of the Indian Subcontinent. Oxford University Press, New Delhi, 556 pp.

James, F.C. & H.H. Shugart (1970). A quantitative method of habitat description. Audubon Field Notes 24: 727–736.

Khan, I. (1992). Distribution and crop raiding behaviour of Nilgai in western U.P. in the village of Aligarh district. M.Phil. Dissertation. Aligarh Muslim University, Aligarh, 81 pp.

Khan, K.A. (2014). Current status and distribution of Nilgai in Aligarh District. M.Phil. Dissertation. Aligarh Muslim University, Aligarh, 89 pp.

Kour, D.N. (2016). Ecobiology of some species of Columbiformes from Jammu. PhD Thesis. University of Jammu, Jammu, 976 pp.

Liebezeit, J.R. & T.L. George (2002). Nest predators, nest-site selection, and nesting success of the Dusky Flycatcher in a managed ponderosa pine forest. The Condor 104(3): 507–517.

MacKenzie, D.I. & S.G. Sealy (1981). Nest site selection in eastern and western kingbirds: a multivariate approach. The Condor 83(4): 310–321.

McConkey, K.R. & D.R. Drake (2002). Extinct pigeons and declining bat populations: are large seeds still being dispersed in the tropical Pacific? pp. 381–395. In: Seed dispersal and frugivory: ecology, evolution and conservation. Third International Symposium-Workshop on Frugivores and Seed Dispersal, São Pedro, Brazil, 6–11 August 2000.

McConkey, K.R., H.J. Meehan & D.R. Drake (2004). Seed dispersal by Pacific Pigeons (Ducula pacifica) in Tonga, Western Polynesia. Emu 104: 369–376.

Meehan, H.J., K.R. Mcconkey & D.R. Drake (2005). Early fate of Myristica hypargyraea seeds dispersed by Ducula pacifica in Tonga, Western Polynesia. Austral Ecology 30(4): 374–382.

Mudappa, D.C. & R. Kannan (1997). Nest-site characteristics and nesting success of the Malabar Gray Hornbill in the southern Western Ghats, India. The Wilson Bulletin 109(1): 102–111.

Owens, I.P. & P.M. Bennett (2000). Ecological basis of extinction risk in birds: habitat loss versus human persecution and introduced predators. Proceedings of the National Academy of Sciences 97(22): 12144–12148.

Qureshi, M.Q. (1991). Population status and movement of nilgai around the village Ghursikaran near Aligarh University. M.Phil. Dissertation. Aligarh Muslim University, Aligarh, 72 pp.

Sieg, C.H. & D.M. Becker (1990). Nest-site habitat selected by Merlins in southeastern Montana. The Condor 92(3): 688–694.

Somasundaram, S. (2006). Status and Ecology of the Nilgiri Wood Pigeon in the Western Ghats. PhD Thesis. Bharathiar University, Coimbatore, 157 pp.

Thornton, I.W., S.G. Compton & C.N. Wilson (1996). The role of animals in the colonization of the Krakatau Islands by fig trees (Ficus species). Journal of Biogeography 23(4): 577–592.

Walker, J. (2007). Geographical patterns of threat among pigeons and doves (Columbidae). Oryx 41(3): 289–299. https://doi.org/10.1017/S0030605307001016

Yasmin, S. (1995). Ecology and Biology of the Indian Peafowl, Pavo cristatus in the Aligarh region. PhD Thesis. Aligarh Muslim University, Aligarh, 129 pp.