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Impact on Veterinary Painkiller () on Black

The Cinereous Vulture, monachus, formerly known as the , is classified as near-threatened at world level (Collar et al. 1994). A. monachus is widely distributed, with a continuous range extending from Europe and North Africa through the to and (Appak, 1992). It has since been extirpated in most of its European range. Its only remaining stronghold in Europe is in . Populations exist in (20 pairs), (1-2 pairs), (100-500 pairs), Mallorca (70 ; 4-5 pairs), and (4 pairs). The entire European population is estimated at between 1,100 and 1,500 pairs (Edward, 1998). There is little data regarding its status in the East but it is the largest of the Old World raptors. The Cinereous Vulture is popularly known in as “XiaGuo” or “-headed Vulture” and in Northern China as “Mountain ”, “Gucha” in Qinghai. Records of it being kept in parks date back over a long time, but give no data on breeding. It is also called “Hairless Vulture”, due to the naked appearance of the head and neck, covered with brown plumules. In the Tibet region the names “God ”, and in Mongolia “Grand Eagle” show that it is an object of religious veneration (Ye Xiao-Ti, 1991).

On characteristics, the species has a massive bill, short neck, extremely long and broad wings, and short tail. The wing span ranges from around 8 feet (2.44m) to 9 1/2 feet (2.90m) and weight varies from around 15lbs (6.80kg) to as high as 27lbs (12.25kg). Females are generally the larger sex. Sexes are almost similar in appearance, with no seasonal variations. Adult plumage is a uniform sooty-brown (Edward, 1998). Head skin and neck are rather dark and the head is covered with a thick downy feather which tends to give the rear of the crown a tufted appearance (Hiraldo, 1983). The Cinereous Vulture forages over many types of habitat including semi-desert and to upland grasslands and bare mountains. It tends to breed below 3,500 feet (1,066m) in Europe and below 7,000 feet (2,133m) in the Asian portion of its range. The species prefers arboreal nest sites, but occasionally uses rock ledges or crags and feeds on carrion, mainly from medium to large carcasses. It will rarely take live prey, but will take injured sometimes. It is dominant over all other Vulture species at a carcass. Conservation Status listed in Appendix II “Threatened”, a species likely to move into the “Endangered” category in the near future. In the Indian sub-continental, for the first time, discussions were held about the conservation and population aspect for this species.

1 / 4 Impact on Veterinary Painkiller (Diclofenac) on Black Vulture

Rajasthan is most important area of Vulture concern. This state is attached with in the North and North south area with Gujarat (Ran of Kach). In the largest dead dumping site is situated in the District of Rajasthan. We are monitoring all ’ species population at this feeding site. Over 3 years (2009-2012) in winter (November to February) population counting was undertaken to assess the importance of this particular site.

Methods For Vulture counting we use standard methods; Bibby et al., (2000); Nichols et al., (2000) and Ralph & Scott (1981)) utilising standard report forms which are completed for all visits, recording the date of the visit, transit line name and locations. We are using this methodology for the counting of Vultures in the morning (07h30–09h30) and afternoon (13hr30-15hr30) with line transit. In our survey period we also record the total number of dead animals arriving daily on the dumping site and their utilisation stage.

Result Total number of population of A.monachus in Jorbeer dumping site means values of different line transit in mid months (Table below). Highest population of Cinereous Vulture reported was 65 in December, 2012. Veterinary use of Diclofenac, a non-steroidal anti-inflammatory drug (NSAID), is the main factor responsible for the declines of species of Vultures in South . Studies have established that Diclofenac is toxic to Vultures ( et al., 2004; et al., 2006) and is widespread in carcasses across India (Taggart et al., 2007) at sufficient concentrations to be the principal cause of the declines (Green et al., 2006, 2007).

Age wise data of Cenereous Vultures in December*

2007 2008 2009 2010 2011 2012

Adult Birds 20 22 28 35 15 50

Juvenilew 8 13 14 20 20 15

Total Birds 28 35 42

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55 35 65

Proportion A/J 2,5 1,69 2 1,75 0,75 3,33

* Extreem population in this month

During 2000-2002 showed 28 cases of Avian Gout, while 17 samples did not exhibit Avian Gout in Pakistan (Oaks et al., 2004). The major concern arising from this availability of dead specimens of A. monachus was not only the fact of discovery after the ban of Diclofenac, but the widespread availability of Diclofenac for sale for veterinary use after the June 2006 ban. In recent years the use of NSAID’s (veterinary painkiller- Diclofenac) for animal treatment has led to the poisoning of a number of Vultures and their breeding rate has declined. In context, the effect of veterinary painkiller (Diclofenac) was apparent in 3 dead specimens of A. monachus collected in February 2012 and again 2 dead specimens of A. monachus was reported in March 2012 during the vulture survey in the municipality of the dead animal dumping site (Jorbeer) (71054 and 74022 East longitude and 270 11’ and 290 03’ North latitudes). In the year 2012, we found about 90 similar cases in 4 vulture species , Neophron percnopterus, Indian , Gyps fulvus, Himalayan Griffon, Gyps himalayensis, and Cinereous Vulture Aegypius monachus, and one raptor, , Aquila nipalensis, affected by the dumping of dead animals contaminated by Diclofenac. For the protection of important Vulture’s species we need more open and safer food zones.

Acknowledgments We would like to thank my co-worker Mr. Deeraj and Mr. Hanesh for their help during the fieldwork and for various rescues of afflicted birds. I also thank the Forest Department for their wonderful support and providing zoo facilities after rescue operations.

Dr Dau Lal Bohra [email protected]

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References Appak, B. A. 1992. Status of the Cinereous Vulture population in . In Protection and study of rare and endangered animal species in nature reserves. Moscow: Collection of Scientific Papers. Collar, N. J., Crosby, M. J. and Stattersfield, A. J. (1994) Birds to watch 2: the world list of threatened birds. Cambridge, U.K.: BirdLife International (BirdLife Conservation Series no.4). Edward N. Diebold. 1998. Cinereous Vulture - Aegypius monachus. (1-3): American Zoo and Aquarium Association. Green, R.E., Taggart, M.A., Das, D., Pain, D.J.,Sashikumar, C., Cunningham, A.A. & Cuthbert, R. 2006. Collapse of Asian vulture populations: risk of mortality from residues of the veterinary drug diclofenac in carcasses of treated cattle. Journal of Applied Ecology, 43, 949–956. Green, R.E., Taggart, M.A., Senacha, K.R., Pain, D.J., Jhala, Y. & Cuthbert, R. 2007. Rate of decline of the oriental whitebacked vulture Gyps bengalensis population in India estimated from measurements of diclofenac in carcasses of domesticated ungulates. PLoS ONE, 2(8), e686, do:10.1371/journal.pone.0000686. Hiraldo, F. 1983. Breeding biology of the Cinereous Vulture. Pp.197–213 in S. R. Wilbur and J. A. Jackson, eds. Vulture biology and management. Berkeley: University of California Press. Swan GE, Cuthbert R, Quevedo M, Green RE, Pain DJ, et al. 2006 Toxicity of diclofenac to Gyps vultures. Biology Letters, doi:10.1098/rsbl.2005.0425. Taggart, M.A., Senacha, K., Green, R.G., Jhala, Y.V., Raghavan, B., Rahmani , A.R. et al. 2007. Diclofenac residues in carcasses of domestic ungulates available to vultures in India. Environment International, 33, 759–765. Oaks JL, Gilbert M, Virani MZ, Watson RT, Meteyer CU, et al. (2004) Diclofenac residues as the cause of vulture population declines in Pakistan. Nature 427: 630–633. Ye Xiao-Ti .1991. Distribution and status of the cinereous vulture Aegypius monachus in china. Birds of Prey Bulletin No 4.51-56 Bibby, C.J., Burgess, N.D., Hill, D.A., and Mustoe, S.H. .2000.. Bird Census Techniques, 2nd ed. Academic Press, London. Nichols, J.D., Hines, J.E., Sauer, J.R., Fallon, F., Fallon, J., and Heglund, P.J. 2000. A double-observer approach for estimating detection probability and abundance from avian point counts. The Auk, 117, 393–408. Ralph, C. J. and Scott, M. J. (eds) .1981. Studies in Avian Biology: Estimating Numbers of Terrestrial Birds, Cooper Ornithological Society, Kansas, USA, vol. 6, pp. 1–630

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