SOUTH ASIA VULTURES: CATASTROPHIC DECLINES AND ENVIRONMENTAL IMPACT
The Meeting Rooms, The Zoological Society of London, Regent’s Park, London NW1 4RY
Chair: Andrew Routh, Chief Veterinary Officer, ZSL
Declines in large raptors Jemima Parry-Jones MBE, Director of the International Centre for Birds of Prey
Global y the large raptors are under threat. Habitat decline, increasing human populations,
lead poisoning, tribal medicine, legal and il egal trade, shooting, electrocution and other
causes contribute to the decline of raptors, particularly the large eagles and vultures.
Although many species stil may not be listed as vulnerable or endangered, by definition
they most likely are. After al , fish rely on water to survive, without water there are no fish.
Similarly if particular species rely on a particular habitat and that is being destroyed then
common sense tel s us that the species in question are going to decline.
One of the downfal s of the larger raptors is that they are long-lived, slow to reproduce and
produce low numbers of young, and thus are less adaptable than smal er species, such as
Sadly, there are many examples. Probably the best known is the California condor, which
was brought to extinction in the wild in the 1980s. It was only when a $3 mil ion a year
programme was instigated that the real cause was discovered to be lead poisoning from
My introduction to the rest of this programme this evening was through the Parsis, who
traditional y have their dead eaten by vultures, however in the 1990s that was no longer
happening … little did we know at that time that diclofenac was the problem.
Diagnosing the cause of the Asian vulture decline Rhys Green, RSPB & University of Cambridge
Large populations of three species of vultures endemic to south Asia existed in the Indian
subcontinent until the early 1990s. Then a very rapid decline began which left only a few
percent of the original numbers alive by the year 2000. The declines have continued since
then and have been especial y rapid for the Oriental white-backed vulture, whose
population in the subcontinent in 2007 was estimated to be about one-thousandth of what
it had been 15 years earlier. Population surveys showed that the rate of decline was so
rapid that an increased death rate of adult birds must be its main mechanism. Post mortem
examinations showed that the majority of dead vultures had visceral gout, due to kidney
damage. The realisation that diclofenac, a non-steroidal anti-inflammatory drug that can
cause kidney failure in birds, had become a widely used veterinary medicine led to the
identification of diclofenac poisoning as a potential cause of the decline. Dead vultures
with gout al had traces of diclofenac in their tissues. Vultures treated experimental y with
the drug died with gout and the same kidney damage as dead birds found in the wild.
Surveys of diclofenac contamination of dead domestic ungulates left for scavengers in
India, combined with vulture population model ing, show that the level of diclofenac
contamination was sufficient for it to be the sole cause of the decline and that there is little
scope for other causes to have contributed much. Removal of diclofenac from the food
supply of vultures and its replacement with a non-toxic alternative is a prerequisite for
Finding solutions to the vulture conservation crisis
The population col apse of vultures in Asia has created an urgent need for solutions to this
conservation crisis. An inter-linked programme of work has focused on conservation
advocacy, applied research, the creation of “vulture safe zones” and captive breeding
centres in order to halt the decline in vulture numbers. Advocacy work has focused at
government level policies as wel as working at “grassroots” with farmers and vets, in order
to spread the message about the role of diclofenac and vulture conservation. In 2006, the
governments of India, Nepal and Pakistan announced a ban on the importation and
production of veterinary diclofenac. In order to facilitate the diclofenac ban, it was
necessary to find an alternative drug effective for treating cattle but of low toxicity to
vultures. Questionnaire surveys of veterinarians, zoos and bird of prey centres on the
treatment of vultures, raptors and other scavenging birds identified the drug meloxicam as
a potential safe alternative to diclofenac, and also established toxicity concerns for other
compounds. A programme of safety testing with meloxicam, undertaken in Southern Africa
and India, established that meloxicam administered at the estimated maximum levels of
exposure caused no adverse reactions in either the African or Asian vulture species.
Meloxicam is now being promoted as a safe alternative drug in Asia with increasing
numbers of companies manufacturing this product. Research is also underway to monitor
the prevalence of diclofenac in livestock carcasses across Asia and to monitor vulture
numbers, so that the effectiveness of the ban at protecting vultures can be accurately
assessed. Efforts are underway to protect smal remaining vulture populations through the
creation of “vulture safe zones” around surviving breeding colonies. A programme of
diclofenac removal from areas surrounding colonies, local level advocacy work, providing
safe food at the colonies and community involvement has provided early encouraging
signs of success with numbers of breeding vultures increasing. Ongoing research is
underway to determine the likely long-term effectiveness of this work. Due to the speed
and scale of the population declines the capture and captive breeding of vultures was
essential in order to prevent the extinction of vultures in the wild. The remote areas where
vultures remain and the vertical cliffs and large trees that vultures nest in has created
chal enging conditions for the safe capture and transport of these birds to the breeding
centre. Teams of climbers and trappers in India and Nepal have now captured over 200
vultures for the centres, providing a vital core population for the captive breeding
Ensuring the Future – the role of conservation breeding and reintroduction Nick Lindsay, Senior Curator – Zoo Projects, ZSL
One of the main actions of the South Asia Vulture Recovery Programme is to establish
populations of the Oriental white-backed vulture (OWBV), the long-bil ed vulture (LBV) and
the slender-bil ed vulture (SBV) in a safe environment, away from diclofenac. A number of
vulture conservation breeding centres are now operational in India, Nepal and Pakistan
with the eventual aim that these centres wil be able to hold sufficient numbers of each
species to ensure that populations can be re-established in the wild.
The programme has been able to use the considerable experience of managing and
breeding vultures available in zoos and other breeding centres to establish the vulture
breeding centres. However, as this is the first project that has worked with such large
numbers of vultures, it wil take some years before the best management strategies for
each species is ful y understood. Over the past 5 years the main aims have been to col ect
wild vultures for the centre and to train local personnel to manage these birds in the
To ensure there wil be a viable population of each species in the long term (15–20 years)
the aim is to work with at least 150 pairs of each species considering that these are long-
lived vultures which produce only one egg per year and take 4–5 years to reach sexual
maturity. Currently there are 3 centres in India and one each in Nepal and Pakistan. With
plans to develop new centres based on existing populations of Oriental white-backed
vultures in zoos in India there should be sufficient space to meet these needs.
The ultimate goal is to produce enough young vultures each year to enable the re-
establishment of populations once the environment is free of diclofenac. Although this may
be some years away it is important to start to plan for the future and identify potential
release sites. This in itself is a huge chal enge but possibly the greatest chal enge facing
the programme is that of resources. Funding the centres over an extended period is key to
the success of the programme but this is going to require a massive investment.
Miércoles, 27 de febrero 2002 B.O.C. y L. - N.º 41 II. DISPOSICIONES GENERALES Segunda.– El presente Decreto entrará en vigor al día siguiente de supublicación en el «Boletín Oficial de Castilla y León». Valladolid, a 21 de febrero de 2002. DECRETO 26/2002, de 21 de febrero, por el que se aprueba el Regla - mento deColegios Profesionales de Castilla y León. La Ley 8/1
Appetizers Marinated prawns and scallops tossed in lemon grass, King prawn with thai basil, chilli and lime Thai spiced king prawn hot pot with lime & chilli King prawn in x.o chilli hot pot (golden sand)King prawns stir ‘w’ diced chicken fried dry onions, x.o paste Steam dumplings ‘w’ glass noodles served in a hot potEggplant stuffed with seafood mince coated