A record of White-rumpedvulture (Gyps bengalensis) nesting in Ahmedabad and Surendranagar districts of Gujarat.

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Original Paper ISSN: 2321-1520 A record of White-rumpedvulture (Gyps bengalensis) nesting in Ahmedabad and Surendranagar districts of Gujarat. Moradiya Mital and Jhala Devendrasinh* *Department of Zoology, University School of Sciences, Gujarat University, Ahmedabad. E-mail Id: ddjhala@gmail.com *Corresponding Author Received Date : 17-2-2018 Published Date : 7-3-2018 Abstract Vultures are scavengers and flesh-eating raptors which soar at very high altitude as well as clean carcass dumping site efficiently. But unfortunately, vulture population have been declined globally as well as regionally due to the use of diclofenac drug in veterinary. In India, after diclofenac ban in year 2006 the declined of vulture population had slow down. On the other hand, to improve the breeding success and restore the damage that already been done to this K- selected population, it is very important to identify causes behind the breeding and nesting failure. In effort to identify reasons behind it we conducted this study and identify probable reasons of nesting failure. Moreover, tree preferences for nesting by White-rumped Vultures in Ahmedabad and Surendranagar were also evaluated and suggested that plantation of those trees near feeding sites may provide more nesting sites to these species. In this study we observed 58.69% nest failure at different stages and among these the nestling largely covered with white feathers/downs (Stage 3) was most vulnerable. Furthermore, during our repeated observations, it is inferred that the environmental and anthropogenic pressure have also induced nest failure during their growth so, consideration should also be given to it. Keyword:Vulture; Gyps bengalensis; Nesting success. Introduction Vultures are one of the larger raptors that soar highest in the sky. They have coexisted with 3

other species, including humans, since time immemorial. Congregating in large number over their feeding places, usually a dead carcass, vultures are known as efficient scavengers playing a crucial role in the recycling of nutrient in nature s food webs (Pandey and Jethva, 2007). The Whiterumped Vulture (WRV) Gyps bengalensis was once described as the commonest species of vulture found in the Indian sub-continent (Gilbert et al., 2006). The populations of vultures have been declined globally as well as regionally rapidly during the mid-1990s due to the contamination of ungulate carcasses with a veterinary drug diclofenac. But the decline of Gyps bengalensis in India has slowed after ban on veterinary use of drug diclofenac. Populations of Gyps bengalensis remained at a low level, but the decline had slowed and may even have reversed both in India and Nepal (Kamboj et al., 2016). However, estimates of the most recent population trends are imprecise, so it is possible that declines may be continuing, though at a significantly slower rate (Prakash et al., 2012; Kamboj et al., 2016). Hence, this study was carried out to know the nesting status of Gyps bengalensisin Ahmedabad and Surendranagar districts of Gujarat State. Methodology and Study Area The observation of nesting of White-rumped Vulture was confined to Ahmedabad and Surendranagar districts of Gujarat State. The observations were made mainly during breeding season of the species. The nests of the species were surveyed extensively during October, 2014 to May, 2015 The colonies of WRV was located and identified. The coordinates of the location of each nest was recorded through GPS (Model: GARMIN etrex Venture HC). Various parameters such as height of nests, tree girth and tree species were record using Bushnell (SIMMONS) Range Finder. Temperature and relative humidity measures by using Extech 45170 Hygro-Thermo- Anemometer-Light meter. Tree species used as substratum to build nest were also noted down. The observations were repeated at interval of 12-15 days. To simplify the analysis of collected data, the nest was classified into 6 stages in this study. Stages of nests were coded as mentioned in the Table 1 and these coding was used to identify the stages at which nest failed. If nestling died in between any of the mentioned stages or if nest was destroyed then it is considered as nesting failure stage (NFS). Table 1: Proposed stages of nest in White-rumped Vulture. Stage No. Proposed Stage Name Stage Code 1. Nest building stage NBS 2. Incubation stage INS 3. Nestling largely covered with white feathers/downs NWF 4. Nestling with dark wings but many white feathers visible on the NDW back and tail 5. Full grow n nestling FGN 6. Nestling flew out from the nest NFO 4

Jhala & Moradiya Results A total of 46 nests of White-rumped Vulture were recorded from the study area. Among them, 15 were in Ahmedabad district and 31 were in Surendranagar district. The nest building period was observed to be during October and November. The most used tree species as substratum for nest was Neem (Azadirachataindica) (21 nests), followed by Ambali (Tamarindusindica), Banyan (Ficusbenghalensis), Khijado (Prosopis cineraria), Peepal (Ficusreligiosa), Jamun (Syzygiumcumini), Palm (Borassusflabellifer) and Shirish (Albizialebbeck) (Fig. 1). Most of the nest build up on the edge of the tree and at top of the tree but very few were in the middle of the tree. Figure 1: Tree species preferred for nest building by White-rumped Vulture in study area. Out of the total 46 recorded nests, 27 nests were successful i.e. completed all six stages mentioned in Table 1, whereas reaming 19 nests were failed. In Ahmedabad, out of the total 15 nests only 8 nests showed successfully completion of all stages, whereas, 7 nests were failed. Likewise, in Surendrangar out of the total 31 nests, 19 nests were successful. It revealed that nesting success rate was 53% and 61% in Ahmedabadand Surendranagar respectively (Fig. 2). Beside nest failure and success record it was also noted that at which stage of nest the failure occurred. It was observed that the failure of nest was between stage 1 and stage 3 (i.e. NBS, INS and NWF). Among these three stages the maximum rate of failure (52.63%) was observed in stage 3 as compared to stage 1 (10.53%) and stage 2 (36.84%). On the contrary, none of the nest fail in stage 4 (NDW), 5 (FGN) and 6 (NFO) (Fig. 3). 5

Figure 2: Nesting success ratio in Ahmedabad and Surendranagar. Figure 3: Number of failure nest at particular stage (NBS = Nest building stage; INS = Incubation stage; NWF = Nestling largely covered with white feathers/downs). Discussion It is well-known that population of Gyps vultures in South Asia have been significantly decreased since the introduction of veterinary use of Diclofenac sodium in the 1990s (Prakash et al., 2003; Green et al., 2004; Prakash et al., 2007; Prakash et al., 2012). This is the single most important reason for the decline of vultures in India, Nepal and Pakistan. So, it is very important to know the current status and probable ways to increase the number of vultures. The data related to breeding and nest building in nature is also helpful to manage and improve the number of vultures. Among different vulture species, the nesting of Gyps bengalensis was evaluated during this study. 6

Jhala & Moradiya Present study divided the process of nestling development into six major stages to know the most fragile period during development. The present study recorded 46 nests of White-rumped Vulture built on 8 different tree species in Ahmedabad and Surendranagar districts of Gujarat. In these regions some dominating and tall trees are Neem, Ambali, Khiado, Banyan and Peepal on which White-rumped Vulture built nest. Generally, lofty and sparsely branched trees in the forest area were used by vultures for nesting and roosting. Such trees provide a better view of surroundings (Yamac, 2007). In our study most of the nests made up of dry twigs, sticks and leaves. White-rumped Vulture build nest during months of October and November on the edge or at the top of the tall trees like Neem, Ambali, Khiado, Banyan, Peepal, Jamun etc., because of their easy takeoff and landing flights. Hence,it is recommended that these tall trees should not be disturbed during months of October and November surrounding the feeding and traditional nesting sites. Moreover, trees of these species planted near feeding sites may provide habitat preference to the species which result into increase the number of White-rumped Vulture. By the observations of nesting success and failure, it was inferred that the maximum number of nests failed in the stage 3 (NWF) when nestling largely covered with white feathers/downs. It may be due to vigorous food consumption during this stage for their growth and less food availability in nearby area. So, parents were unable to fulfill the requirements of rapid growth of nestling during this stage leads to weakness and prone to infections of pathogens. As compared to previous records of Pandey and Jethva (2007) the number of nests decreased in Ahmedabad may be due to rapid urbanization and more human vulture conflict. On the other hand, number of nests increased in Surendrangar due to more food availability along with good vegetation of tall trees near feeding sites and less human vulture conflict. It was also possible that the fledging of White-rumped Vulture facing dehydration problem during summer (March to May) in the study area. Fledging which affected form dehydration they were weak and unable to fly easily and some had injuries as they fall down from their nests. Another important recommendation to prevent dehydration is to create a shallow artificial water bodies near vulture feeding and nesting sites. Conclusion Though the population of White-rumped Vulture is still declining since 1990s, the rate of decline is reduced. However, as the species is K-selected species, breeding success is also important for the recovery of the species in nature. The present study reveals that the nesting success was average about 57% collectively in Ahmedabad and Surendranagar districts, which means that it required species attention for the conservation of this scavenger. Among various stages the most important stage to take care was stage-3 i.e. Nestling largely covered with white feather/downs (NWF) due to high mortality was recorded in this stage. References Gilbert M, Watson RT, Virani MZ, et al. (2006) Rapid population declines and mortality 7

cluster in three Oriental White-backed Vulture Gyps bengalensiscolonies due to diclophenac poisoning. Fauna and Flora International.40(4): 388 399. GreenRE, Newton I, Shultz S, et al. (2004) Diclofenac poisoning as a cause of vulture population declines across the Indian subcontinent. Journal of Applied Ecology.41(5): 793 800. Kamboj RD, Tatu K, Munjpara SB. (2016) Status of Vulture in Gujarat-2016.Gujarat Ecological Education and Research (GEER) Foundation, Gandhinagar. Pandey CN,Jethva B. (2007) Status of vultures in Gujarat state-2007. Gujarat Ecological Education and Research (GEER) Foundation, Gandhinagar. Prakash V, Pain DJ, Cunningham AA, et al. (2003) Catastrophic collapse of Indian white-backed Gyps bengalensis and long-billed Gyps indicus vulture populations. Biological Conservation. 109(3): 381 390. Prakash V, Green RE, Pain DJ, et al. (2007) Recent changes in populations of resident Gyps vultures in India. Journal of The Bombay Natural History Society. 104(2): 127 133. Prakash V, Bishwakarma MC, Chaudhary A, et al. (2012) The population decline of Gyps vultures in India and Nepal has slowed since veterinary use of diclofenac was banned. PLoS One. 7(11): e49118, 1-10. Yamac E. (2007) Roosting tree selection of Cinereous Vulture Aegypiusmonachusin breeding season in Turkey.Podoces. 2(1): 30 36. 8