Reduced Food Availability Induces Behavioural Changes in Griffon Vulture Gyps Fulvus

Total Page:16

File Type:pdf, Size:1020Kb

Reduced Food Availability Induces Behavioural Changes in Griffon Vulture Gyps Fulvus Ornis Fennica 87:00–00. 2010 Reduced food availability induces behavioural changes in Griffon Vulture Gyps fulvus Iñigo Zuberogoitia, José E. Martínez, Antoni Margalida, Imanol Gómez, Ainara Azkona & José Antonio Martínez I. Zuberogoitia, 1-Estudios Medioambientales Icarus S.L. Pintor Sorolla 6, 1° C., E- 26007 Logroño, Spain. E-mail [email protected] J.E. Martínez, Bonelli’s Eagle Study and Conservation Group. Plaza de Toledo, 10-5E, E-30009 Murcia, Spain A. Margalida, Bearded Vulture Study and Protection Group, Apdo. 43, E-25520 El Pont de Suert, Lleida, Spain I. Gómez & A. Azkona, Sociedad para el Estudio de las Aves Rapaces (SEAR). C/ Kart Marx, 15, 4° F., 48950 Erandio, Bizkaia, Spain J.A. Martínez, Juan de la Cierva 43, El Campello, E-03560 Alicante, Spain Received 12 august 2009, accepted 17 November 2009 In natural conditions, Griffon Vultures typically show shy behaviour and escape by flying if approached by humans. According to the state-dependent foraging theory, Griffon Vul- tures should modify their foraging behaviour depending on food availability and preda- tion risk, humans being the main potential predator. We tested the Reaction Time (RT) and Flight Initiation Distance (FID) in five different artificial feeding schemes over three years in which food availability in the field varied significantly. The first scenario was set in a so-called “vulture restaurant”, in which government employees feed vultures that may exhibit tame behaviour and stay within a few meters from a feeding person. Scenario 2 involved similar conditions, but here the researchers not employees placed the food in the vulture restaurant. The vultures did not land at the restaurant until one day had passed, and they flew away when people approached them within 250 m. The third scenario was established in a local zoo several months after the closure of the vulture restaurant. Here, employees fed captive vultures that were often accompanied by wild birds that landed to take food. The RT was 14.2 min and the FID was 50 m. The fourth scenario was estab- lished during the subsequent breeding season in a mountain where vultures were fed by the authors of the present study. The RT was 2.8 min and the FID was 15.2 m. The fifth scenario was established in another mountain after the breeding season. Now, the RT was 19.2 min and the FID was 52.2 m. These results demonstrate the ability of vultures to eval- uate the predation risk depending on food availability and their state of hunger, and their ability to modify their behaviour from “natural” caution (”shyness”) towards a more toler- ant (”fearless”) behaviour. 2 ORNIS FENNICA Vol. 87, 2010 1. Introduction ture Cathartes aura also live in cities, but this is not true for European vultures that have suffered Foraging occupies a substantial amount of the from human persecution for centuries (Donázar daily time budget of every animal species. In such 1993). In Spain, for example, Griffon Vultures cases, for a foraging animal, the optimal behaviour Gyps fulvus were killed as pests until 1966 after may vary both with the quality of the foraging which they have been protected by law (Donázar patch and with the internal state of an individual 1993). Nonetheless, farmers, shepherds and hunt- (McNamara & Houston 1986). This variation ers continued to poison and directly persecute vul- leads to a trade-off between energy gains and pre- tures until recently (Olea et al. 1999, Hernández & dation risk (Olsson et al. 2002). Individuals tend to Margalida 2008, Margalida et al. 2008, Hernández reduce the risk of predation by altering their be- & Margalida 2009). This activity has decreased haviour (Houston & McNamara 1989). However, since the banning of poison use in 1984, after food limitations may force animals to evaluate the which the Spanish population has been recovering trade-offs between predation risk and fitness, and increasing (Parra & Tellería 2004). From the which may depend on their future expectations 1980’s to the 1990’s, the Griffon Vulture popula- (i.e., breeding success and survival; Olsson et al. tion and distribution has rapidly increased, largely 2002). thanks to feeding them at feeding stations (artifi- Animals may start behaving tamely or show cial “vulture restaurants”) and to the active protec- habituation in the absence of predators (Blumstein tion of vulture breeding areas (Del Moral & Marti et al. 2004) when, for example, no aggressive in- 2001). ter-specific interactions occur for long periods of Food is a limited resource for birds, affecting time (Coleman et al. 2008). On remote islands, survival, breeding and behaviour (Lack 1954, wild animal species may not fear humans or terres- Newton 1998). The behavioural reaction to varia- trial predators because they have often not experi- tion in food supply has been documented for sev- enced negative impacts that would normally lead eral bird species (Poulin et al. 1992, Brown & them to become alert and escape from a threaten- Sherry 2006, Robb et al. 2008) and is related to ing situation (Rödl et al. 2007). Such behavioural predation risk (Olsson et al. 2002). However, until pattern is problematic for native animals that do now few studies have assessed vulture behaviour not recognize threats from introduced predators in relation to food availability. Due to sanitary re- (Massaro et al. 2008), and it also makes it difficult strictions, vulture conservation in Europe is pres- for individuals to adapt their behaviour to new ently conditioned by supplementary feeding activ- threats (Blumstein et al. 2004). In areas with in- ities (Donázar et al. 2009a, b). Little is known, creasing human use, some species have adapted however, if these activities lead to behavioural their behaviour to obtain the benefits of living changes in vultures, which could in turn be rele- close to humans, their behavioural flexibility hav- vant to vulture conservation. ing been conditioned by a favourable situation in The present study was done in an area where which humans do not show or show only little an- Griffon Vultures do not depend on feeding sta- tagonistic behaviour. Such adaptations are obvi- tions, and where extensively raised livestock pro- ous in urban areas, with pigeon Columba species, vide the biomass required to ensure the survival of gull Larus species, rats (e.g., Rattus norvegicus), the local population. The systematic removal of sparrow Passer species and crow Corvus species livestock from the mountains and the closing of serving as good examples. Some birds of prey vulture feeding stations in neighbouring provinces have adapted to living close to humans by using have caused the local population to decline, with a buildings to nest (Cade & Burnham 2003, Ellis et simultaneous decrease in breeding parameters al. 2009) and by hunting in gardens, orchards, (Zuberogoitia et al. 2009). Moreover, mortality parks and even streets (Van Nieuwenhuyse et al. due to starvation has become increasingly com- 2008). Some evasive raptors, such as the Goshawk mon in recently fledged birds of some vulture col- Accipiter gentilis, tolerate human activities in cit- onies. Another sign of food shortage is the recent ies (Kenward 2006). New World vulture species increase in formal complaints about vultures at- Black Vulture Coragyps atratus and Turkey Vul- tacking live livestock (Margalida & Campión Zuberogoitia et al.: Behavioural changes in Griffon Vulture 3 Fig. 1. Study area. Colonies of Griffon Vulture (black asterisks) around sites applied for the five scenarios (full circles; see text), and around sites applied for other scenarios during the breeding sea- son of 2008 (hollow circles). 2009). The only existing feeding station in the from the moment food is made available by hu- study area was closed in 2006. Simultaneously, a mans to the moment it is detected by vultures, i.e., policy involving greater control of dead livestock until the first vulture lands to feed; and (2) the in the field was initiated. Flight Initiation Distance (FID), measured as the These changes in food availability due to bo- distance at which feeding vultures allow humans vine spongiform encephalopathy (Donázar et al. to approach them without escaping by flight. We 2009a, b, Zuberogoitia et al. 2009) enabled us to suggest that vultures would adopt a “tame” or develop a behavioural experiment, in which the “fearless” behaviour related to the amount of main hypothesis was as follows: according to the available food. state-dependent foraging theory, the Griffon Vul- ture, a long-lived species that has long survived human persecution, will change its feeding behav- 2. Material and methods iour to maintain high physical fitness according to an artificial feeding programme, i.e., the establish- 2.1. Study area and design ment of feeding stations. Our main goal is to assess the relationship between food availability and for- The study was done west of Biscay, northern aging behaviour of Griffon Vultures by analyzing Spain, between 43°10’and 43°27’N and 3°27’and (1) the Reaction Time (RT), which is the time lag 2°31’W (Fig. 1). The study area is hilly and den- 4 ORNIS FENNICA Vol. 87, 2010 sely populated, with extensive industrial and other tion Time (RT), considered as being the time be- urban areas. More than 50% of the area is allocated tween one vulture flying above a carrion within a 5 to forestry at the expense of traditional small-scale km radius and the first vulture landing, and Flight farming, and the traditional patchwork of wood- Initiation Distance (FID), measured as the distance land, pasture and small holdings has been greatly at which feeding vultures allowed humans to ap- reduced. proach without taking off. In 1986 a “vulture restaurant”, a vulture feed- Scenario 1: Predictable food source in a food- ing station regulated by the local government, was rich environment and habituation to humans.
Recommended publications
  • Vulture Conservation in Asia 30 May 2016, Karachi, Pakistan
    Proceedings of the Regional Symposium on Vulture Conservation in Asia 30 May 2016, Karachi, Pakistan 1 Contents Call for Papers 5 Agenda 8 Paper 1: An overview of recent advances and priorities for vulture conservation in the South Asia region 10 Abstract 10 Background and the formation of the SAVE consortium partnership 10 SAVE Blueprint and annually reviewed priorities 11 SAVE priorities for Asian vulture conservation for 2016 11 A call to action for emerging priority threats to vultures in the region – Veterinary NSAIDs... 12 Aceclofenac 12 Nimesulide 13 Ketoprofen 13 Diclofenac 13 Wider solutions 13 References 14 Paper 2: Vulture Conservation initiatives of WWF-Pakistan 15 Executive Summary 15 Introduction 16 WWF-Pakistan supported vulture studies prior to the GVRP 16 Conservation of Vultures in District Mianwali: a feasibility study 16 Under the Gyps Vulture Restoration Project, the following activities have been conducted so far: 17 Ex situ Conservation: 17 In situ Conservation (Vulture Safe Zone, Nagar Parkar) 17 Plans for 2016 - 2017 20 References: 21 Paper 3: Status and distribution of vultures in Sindh 22 Abstract 22 Introduction 22 Distribution of Vultures in Pakistan 23 Materials and Methods 24 2 Potential Sites 27 Conclusion 30 Priority Actions 31 Acknowledgements: 31 Paper 4: Establishment and management of community-based Vulture Safe Zones (VSZ) in Bangladesh 33 Vulture Safe Zone Declaration Process in Bangladesh 34 Population Census 35 Pharmacy Survey 36 Institutional Mechanism 37 Conclusion 37 References 38 Paper 5:
    [Show full text]
  • Griffon Vultures &Lpar;<I>Gyps Fulvus</I>&Rpar; Ingesting Bones At
    SEPTEMBER1997 LETTERS 287 AravaipaCreek, Arizona. Almost immediatelyat leastsix Elf Owls beganvocalizing from dispersedlocations around our campsiteand at leastfour of them began making low passesat the Great Horned Owl. Before we could relocate the horned owl to a protectedenclosure, it wasstruck once in the head by an Elf Owl. Some nocturnal behaviorsmay not be well known or understood,not becausethey are rare, but becausethey are difficult to observe.This may changewith the increasedavailability of night vision equipment (P. Henson and J A Cooper 1994, Auk 111:1013-1018). Currently, observationsof nocturnal behaviorsare likely to be sporadicand anecdotal,and therefore unreported. Such information, however,may help in understandinga speciesbiology. For example, other researchershave observedgroup mobbing by Elf Owls (F.R. Gehlbach,pers. comm.; B.A. Millsap, pers. comm.), but there are no publishedreports of the behavior.Our observations,and thoseof other researchers, suggestthat Elf Owlswill join together in mobbing and that they can be physicallyaggressive when defending their nestsagainst predators. We thank A. Duerr, T.S. Estabrookand R.L. Spauldingfor assistingwith the observations.We alsothank T. Brush, ER. Gehlbach, R. Glinski, P. Hardy, B.A. Millsap, G. Proudfoot and H.A. Snyder for sharing their observational information concerning mobbing by small owls.This manuscriptbenefitted from the constructivereviews of ER. Gehlbach,C. Marti, B.A. Millsapand an anonymousreviewer.--Clint W. Boal, Brent D. Biblesand R. William Mannan, Schoolof RenewableNatural Resources,University of Arizona, Tucson,AZ 85721 U.S•. j. RaptorRes. 31 (3):287-288 ¸ 1997 The Raptor ResearchFoundation, Inc. GRIFFONVULTURES (GYPS FULVUS) INGESTING BONES AT THE OSSUARIESOF BEARDEDVULTURES ( GYPAETUSBAR•ATUS) Some African vulturesovercome the calcium deficiencyin their diets by ingestingbone fragments,and are depen- dent on the presenceof largepredators to supplythem (Mundy and Ledger 1976, S.
    [Show full text]
  • Griffon Vulture Mortality at Wind Farms in Southern Spain: Distribution of Fatalities and Active Mitigation Measures ⇑ Manuela De Lucas A, , Miguel Ferrer A, Marc J
    Biological Conservation 147 (2012) 184–189 Contents lists available at SciVerse ScienceDirect Biological Conservation journal homepage: www.elsevier.com/locate/biocon Griffon vulture mortality at wind farms in southern Spain: Distribution of fatalities and active mitigation measures ⇑ Manuela de Lucas a, , Miguel Ferrer a, Marc J. Bechard b, Antonio R. Muñoz c a Department of Ethology and Biodiversity Conservation, Estación Biológica de Doñana (CSIC), Av. Américo Vespucio s/n, 41092 Seville, Spain b Raptor Research Center, Department of Biological Sciences, Boise State University, 1910 University Dr., Boise, ID 83725, USA c Fundación Migres, Complejo Huerta Grande, Crta. N 340 Km 97.6, 11390 Pelayo, Algeciras, Spain article info abstract Article history: Wind is increasingly being used as a renewable energy source around the world. Avian mortality is one of Received 22 July 2011 the negative impacts of wind energy and a new technique that reduces avian collision rates is necessary. Received in revised form 14 December 2011 Using the most frequently-killed species, the griffon vulture (Gyps fulvus), we studied its mortality at 13 Accepted 22 December 2011 wind farms in Tarifa, Cadiz, Spain, before (2006–2007) and after (2008–2009) when selective turbine Available online 24 January 2012 stopping programs were implemented as a mitigation measure. Ten wind farms (total of 244 turbines) were selectively stopped and three wind farms (total of 52 turbines) were not. We found 221 dead griffon Keywords: vultures during the entire study and the mortality rate was statistically different per turbine and year Gyps fulvus among wind farms. During 2006–2007, 135 griffon vultures were found dead and the spatial distribution Mortality reduction Energy production of mortality was not uniformly distributed among turbines, with very few turbines showing the highest Turbine stopping program mortality rates.
    [Show full text]
  • Lappet-Faced Vultures Studies at Mahazat As Syed Protected
    Status of Vultures in the Middle East with detailed studies of Lappet-faced and Griffon Vultures in Saudi Arabia Mohammed Shobrak Biology Department, Taif University, Saudi Wildlife Authority, Saudi Arabia Content of the Presentation •Vultures in the Middle East and Arabian Peninsula • Status & Trend & • Griffon Vultures • Lappet-faced Vultures Studies in KSA •Threats •Conclusion and Recommendations Vultures Recoded in the Middle East and the Arabian Peninsula ØBearded Vulture Gypaetus barbatus (Rare Breeding) ØEgyptian Vulture Neophron percnopterus (Breeding) ØGriffon Vulture Gyps fulvus (Breeding) ØLappet-faced Vulture Torgos tracheliotus (Breeding) ØCinereous Vulture Aegypius monachus (the majority are Migratory) ØRüppell’s Vulture Gpys rueppellii (Meinertzhagen 1945) The majority of the Middle Eastern populations are migratory (winter visitor and passing migrants), with small breeding populations in Iran and Turkey. Cinereous Vulture is a winter visitor to the Arabian Peninsula, concentrated at northern, central and eastern part of the Arabian Peninsula. IUCN Red List Species Status at the Population Status Scientific Name Status International (Trend) Global / Reginal Agreement Aegypius monachus CITES II, CMS II, EU WV (Linnaeus, 1758) NT/NT WTR (A), Raptor MoU 1 Decreasing Middle Eastern populations extend from SW Iran into much of Turkey, with more isolated populations in Yemen and SW Saudi Arabia The bearded vulture was a rare resident and now probably no longer breeds in Saudi Arabia, and probably in Yemen (50 breeding pairs were
    [Show full text]
  • Vulture Msap)
    MULTI-SPECIES ACTION PLAN TO CONSERVE AFRICAN-EURASIAN VULTURES (VULTURE MSAP) CMS Raptors MOU Technical Publication No. 5 CMS Technical Series No. xx MULTI-SPECIES ACTION PLAN TO CONSERVE AFRICAN-EURASIAN VULTURES (VULTURE MSAP) CMS Raptors MOU Technical Publication No. 5 CMS Technical Series No. xx Overall project management Nick P. Williams, CMS Raptors MOU Head of the Coordinating Unit [email protected] Jenny Renell, CMS Raptors MOU Associate Programme Officer [email protected] Compiled by André Botha, Endangered Wildlife Trust Overarching Coordinator: Multi-species Action Plan to conserve African-Eurasian Vultures [email protected] Jovan Andevski, Vulture Conservation Foundation European Regional Coordinator: Multi-species Action Plan to conserve African-Eurasian Vultures [email protected] Chris Bowden, Royal Society for the Protection of Birds Asian Regional Coordinator: Multi-species Action Plan to conserve African-Eurasian Vultures [email protected] Masumi Gudka, BirdLife International African Regional Coordinator: Multi-species Action Plan to conserve African-Eurasian Vultures [email protected] Roger Safford, BirdLife International Senior Programme Manager: Preventing Extinctions [email protected] Nick P. Williams, CMS Raptors MOU Head of the Coordinating Unit [email protected] Technical support Roger Safford, BirdLife International José Tavares, Vulture Conservation Foundation Regional Workshop Facilitators Africa - Chris Bowden, Royal Society for the Protection of Birds Europe – Boris Barov, BirdLife International Asia and Middle East - José Tavares, Vulture Conservation Foundation Overarching Workshop Chair Fernando Spina, Chair of the CMS Scientific Council Design and layout Tris Allinson, BirdLife International 2 Multi-species Action Plan to Conserve African-Eurasian Vultures (Vulture MsAP) Contributors Lists of participants at the five workshops and of other contributors can be found in Annex 1.
    [Show full text]
  • The Reintroduction of Eurasian Griffon Monachus Vultures to France
    Chancellor, R. D. & B.-U. Meyburg eds. 2004 Raptors Worldwide WWGBP/MME A Success Story: The Reintroduction of Eurasian Griffon Gyps fulvus and Black Aegypius monachus Vultures to France Michel Terrasse, François Sarrazin, Jean-Pierre Choisy, Céline Clémente, Sylvain Henriquet, Philippe Lécuyer, Jean Louis Pinna, and Christian Tessier ABSTRACT By the end of the 1960s, the future of vultures in France appeared bleak. Apart from the western half of the Pyrenees, with residual populations of Eurasian Griffon Gyps fulvus and Bearded Vultures Gypaetus barbatus, and Corsica with a few Bearded Vultures, most of France had lost its large vultures including the Black Vulture Aegypius monachus. Within the scope of a national conservation campaign, a process to restore raptor communities began. Concerning vultures, this was completed through reintroduction programmes. After the success of the Griffon Vulture reintroduction, started in 1968 in the Grands Causses of the Massif Central, other programmes followed in the 90s: Black Vultures in the Massif Central and then Griffon Vultures in the Southern Alps. In 2003 a viable population of Griffon Vultures in the Massif Central contained around 110 pairs. The same situation occurred in the Alps with about 50 breeding pairs of Griffon Vultures. Ten years after the beginning of the Black Vulture releases, the free ranging population included 11 breeding pairs. Accurate monitoring during the reintroduction period allowed us to estimate demographic parameters such as survival and breeding rates, evolution of breeding and foraging territories, main threats, movements between reintroduced populations and those from neighbouring countries, acceptance by people and the beneficial part played by vultures in what is called sustainable development.
    [Show full text]
  • Recent Literature and Book Reviews
    Vulture News 69 November 2015 RECENT LITERATURE AND BOOK REVIEWS P.J. Mundy BAMFORD, A. J., MONADJEM, A., DIEKMANN, M. & HARDY, I. C.W. (2009). Development of non-explosive-based methods for mass capture of vultures. South African Journal of Wildlife Research 39: 202-208. Investigated methods of launching nets, powered by black powder, detonators, elastic, and compressed air, and a walk-in trap. The last proved most effective at capturing birds, needed no licence, but took a long time to construct and of course was barely portable. (email for Monadjem: [email protected]) BIRD, J. P. & BLACKBURN, T. M. (2011). Observations of large raptors in northeast Sudan. Scopus 31: 19-27. From a 430km transect (Atbara to Port Sudan) and other ad hoc observations, in January 2010, three species of vulture were seen. Thirty Egyptian Vultures on the transect, counts of 21 and 24 Lappet-faced Vultures at a carcass and one Hooded Vulture, were noted. (email: [email protected]) BREWSTER, C. A & TYLER, S. J. (2012). Summary of category B records. Babbler 57: 45-47. Many sightings are listed for the Cape, Lappet-faced, White-headed and Hooded Vultures, but no ages. In the Tswapong Hills, no nests of the Cape Vulture were seen at Lerala, but 76 were seen at Moremi Gorge. On p. 57 many sightings are listed of the White-backed Vulture, from singles up to groups of about 70. c ( /o BLB, Box 26691, Gaborone) 51 Vulture News 69 November 2015 BRUCE-MILLER, I. (2008). Martial Eagle Polemaetus bellicosus apparently killing White-headed Vulture Trigonoceps occipitalis.
    [Show full text]
  • Trade of Threatened Vultures and Other Raptors for Fetish and Bushmeat in West and Central Africa
    Trade of threatened vultures and other raptors for fetish and bushmeat in West and Central Africa R. BUIJ,G.NIKOLAUS,R.WHYTOCK,D.J.INGRAM and D . O GADA Abstract Diurnal raptors have declined significantly in Introduction western Africa since the s. To evaluate the impact of traditional medicine and bushmeat trade on raptors, we ex- ildlife is exploited throughout West and Central amined carcasses offered at markets at sites (– stands WAfrica (Martin, ). The trade in bushmeat (wild- per site) in countries in western Africa during –. sourced meat) has been recognized as having a negative im- Black kite Milvus migrans andhoodedvultureNecrosyrtes pact on wildlife populations in forests and savannahs monachus together accounted for %of, carcasses com- (Njiforti, ; Fa et al., ; Lindsey et al., ), and it . prising species. Twenty-seven percent of carcasses were of is estimated billion kg of wild animal meat is traded an- species categorized as Near Threatened, Vulnerable or nually in Central Africa (Wilkie & Carpenter, ). In add- Endangered on the IUCN Red List. Common species were ition to being exploited for bushmeat, many animals are traded more frequently than rarer species, as were species hunted and traded specifically for use in traditional medi- with frequent scavenging behaviour (vs non-scavenging), gen- cine, also known as wudu, juju or fetish (Adeola, ). eralist or savannah habitat use (vs forest), and an Afrotropical The use of wildlife items for the treatment of a range of (vs Palearctic) breeding range. Large Afrotropical vultures physical and mental diseases, or to bring good fortune, were recorded in the highest absolute and relative numbers has been reported in almost every country in West and in Nigeria, whereas in Central Africa, palm-nut vultures Central Africa.
    [Show full text]
  • Raptors in the East African Tropics and Western Indian Ocean Islands: State of Ecological Knowledge and Conservation Status
    j. RaptorRes. 32(1):28-39 ¸ 1998 The Raptor ResearchFoundation, Inc. RAPTORS IN THE EAST AFRICAN TROPICS AND WESTERN INDIAN OCEAN ISLANDS: STATE OF ECOLOGICAL KNOWLEDGE AND CONSERVATION STATUS MUNIR VIRANI 1 AND RICHARD T. WATSON ThePeregrine Fund, Inc., 566 WestFlying Hawk Lane, Boise,1D 83709 U.S.A. ABSTRACT.--Fromour reviewof articlespublished on diurnal and nocturnal birds of prey occurringin Africa and the western Indian Ocean islands,we found most of the information on their breeding biology comesfrom subtropicalsouthern Africa. The number of published papers from the eastAfrican tropics declined after 1980 while those from subtropicalsouthern Africa increased.Based on our KnoM- edge Rating Scale (KRS), only 6.3% of breeding raptorsin the eastAfrican tropicsand 13.6% of the raptorsof the Indian Ocean islandscan be consideredWell Known,while the majority,60.8% in main- land east Africa and 72.7% in the Indian Ocean islands, are rated Unknown. Human-caused habitat alteration resultingfrom overgrazingby livestockand impactsof cultivationare the main threatsfacing raptors in the east African tropics, while clearing of foreststhrough slash-and-burnmethods is most important in the Indian Ocean islands.We describeconservation recommendations, list priorityspecies for study,and list areasof ecologicalunderstanding that need to be improved. I•y WORDS: Conservation;east Africa; ecology; western Indian Ocean;islands; priorities; raptors; research. Aves rapacesen los tropicos del este de Africa yen islasal oeste del Oc•ano Indico: estado del cono- cimiento eco16gicoy de su conservacitn RESUMEN.--Denuestra recopilacitn de articulospublicados sobre aves rapaces diurnas y nocturnasque se encuentran en Africa yen las islasal oeste del Octano Indico, encontramosque la mayoriade la informaci6n sobre aves rapacesresidentes se origina en la regi6n subtropical del sur de Africa.
    [Show full text]
  • Aegypius Monachus)
    Implementation Review of the EU Species Action Plan for the Cinereous Vulture (Aegypius monachus) LIFE14 PRE UK 002 “Coordinated Efforts for International Species Recovery EuroSAP” Report commissioned by The European Commission Directorate General for the Environment Compiled by Compiler: Jovan Andevski [email protected] Professional review: José Tavares [email protected] Vulture Conservation Foundation, VCF Wuhrstrasse 12. CH-8003 Zurich, Switzerland Date of adoption April 2017 Recommended citation Andevski, J., (2017) Updating the International Species Action Plan for the Cinereous Vulture: Implementation review. Report of Actions A3 under the framework of Project LIFE EuroSAP (LIFE14 PRE UK 002). (unpublished report). 2 Introduction This implementation review report is manly based on data collected though the online questionnaire distributed in late October 2016 (Implementation Review of the Species Action Plan for the Cinereous (Black) Vulture - Aegypius monachus), but it also includes information collected though the Vulture MsAP online questionnaire distributed mid-August 2016 among vulture experts and governmental representatives from the range countries and from the European Vulture Muli-species Action Plan Workshop held in Monfegüe 25-29 October 2016. The two questionnaires and the workshop were shared activities between the “Coordinated Efforts for International Species Recovery – EuroSAP” Life Project, the “Multi-species Action Plan to Conserve African and Eurasian Vultures (Vulture MsAP)” and the Flyway Action
    [Show full text]
  • Rumped Vulture (Gyps Bengalensis ) in and Around Jorbeer Area, Bikaner
    International Journal of Research in Environmental Science (IJRES) Volume 2, Issue 4, 2016, PP 35-39 ISSN 2454-9444 (Online) http://dx.doi.org/10.20431/2454-9444.0204003 www.arcjournals.org The Ecology and Behaviour of Critically Endangered White- Rumped Vulture (Gyps Bengalensis) in and Around Jorbeer Area, Bikaner Dr. Prabodh Chander Khatri Lecturer (Biology), Department of Research, Institute of Advance Study in Education (I.A.S.E.) Bikaner (Rajasthan) [email protected] Abstract: White-rumped vulture was completely migratory vulture at Jorbeer, Bikaner. Now it is disappearing from site. After year 2013 no single white-rumped was observed. Maximum of 7 white-rumped vultures recorded in 15 years of research study. The distribution of the species was recorded in 15 villages covering 1584 Square / Kilometer area between Latitude 27050' North to 28004' North and 73004' East to 73034' East Longitude as home range in Eastern-Southern and South-West part of Bikaner. The spectacular daily activity of white-rumped vulture comprises Feeding 2.72%, Resting 67.42%, Sunning 0.60%, Scratching 0.05%, Disturbance 0.06%, Fighting 0.009% and Flight 27.87% of total day activity. Only one dead vulture and no sick vulture observed during research work. At Jorbeer, feral dogs are main threat for vultures. Medication and effect of any disease was not recorded in vultures. Keywords: White-rumped vulture, Migratory, Disappearing, Feral dogs. 1. INTRODUCTION Vultures have declined from many parts of their former ranges owing to food shortages and loss of habitat (Pain et al. 2003). Since the early 1990s there has been a catastrophic decline in three Gyps species in the Indian subcontinent white rumped vulture, long billed and slender billed vultures1.
    [Show full text]
  • Saving Asia's Gyps Vultures: the "Vulture Rescue" Team's Conservation Programme
    Chancellor, R. D. & B.-U. Meyburg eds. 2004 Raptors Worldwide WWGBP/MME Saving Asia's Gyps Vultures: the "Vulture Rescue" Team's Conservation Programme Vibhu Prakash, Deborah J. Pain, Susanne Shultz and Andrew A. Cunningham ABSTRACT Populations of three species of griffon vultures (Gyps bengalensis, G. indiens , and G. tenuirostris) have declined by more than 90% across India during the last two decades. Results from studies by the Bombay Natural History Society suggest the declines in India are not caused by food shortage, habitat loss or persecution. In 2001, a consortium consisting of BNHS and the Poultry Diagnostic & Research Centre in India (PDRC), and the Royal Society for the Protection of Birds (RSPB), the Institute of Zoology of the Zoological Society of London (ZSL/IoZ) and the National Bird of Prey Centre in the UK, obtained British Government funding (under the Darwin Initiative for the Survival of Species) to (i) investigate the causes of decline through setting up a Vulture Care Centre and diagnostic laboratories in India, (ii) conduct annual nationwide surveys and colony monitoring, and (iii) produce a recovery plan. Nationwide monitoring (so far up to 2002) indicates that Gyps vulture numbers continue to decline due to abnormally low reproductive success and abnormally high mortality rates of all age classes; very fresh carcasses have been collected throughout the country and systematically examined; epidemiological and pathological observations indicate the declines to be due to an infectious disease. A Vulture Care Centre, incorporating a diagnostic laboratory, has been built and was inaugurated in February 2003. Preliminary results from sick vultures housed at this centre appear to endorse the infectious disease hypothesis.
    [Show full text]