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International studbook for the scimitar-horned oryx Oryx dammah Twelfth edition. Current to 31 December 2016 Tania Gilbert, Marwell Wildlife

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  • International studbook for the scimitar-horned oryx

    Oryx dammah

    Twelfth edition. Current to 31 December 2016

    Tania Gilbert, Marwell Wildlife

  • Produced by: Marwell Wildlife Thompsons Lane Winchester Hampshire SO21 1JH United Kingdom Phone: +44 (0) 1962 777407 Fax: +44 (0) 1962 777511 Web: www.marwell.org.uk E-mail: [email protected]

    Compiled and Edited by: Tania Gilbert International Studbook Keeper and EEP Coordinator Citation: Gilbert, T. (2017): International studbook for the scimitar-horned oryx Oryx dammah. Twelfth edition. Marwell Wildlife, Winchester Front cover: Scimitar-horned oryx calf in Dghoumes National Park, Tunisia. Photograph by Robert Cooke, Marwell Wildlife

    mailto:[email protected]

  • Copyright © 2017 by Marwell Wildlife. All rights reserved. No part of this publication may be reproduced in hard copy or other formats without advance written permission from Marwell Wildlife. Members of the World Association of Zoos and Aquariums (WAZA) may copy this information for their own use. The information contained in this studbook has been obtained from numerous sources and is believed to be reliable. However, given the nature of institutional records Marwell Wildlife cannot guarantee the accuracy, adequacy, or completeness of any information. Marwell Wildlife make no warranties or representations of any kind, express or implied including but not limited to warranties of merchantability of fitness for particular purpose. Marwell Wildlife disclaim all liability for errors or omissions that may exist and shall not be liable for any incidental, consequential, or other damages (whether resulting from negligence or otherwise) including, without limitation, exemplary damages or lost profits arising out of or in connection with the use of this publication. The technical information provided in the studbook can easily be misread or misinterpreted unless properly analysed, as such WAZA and Marwell Wildlife strongly recommend that users of this information consult with the Studbook Keeper in all matters related to data analysis and interpretation, and for the most current data.

  • Contents Page 1. Introduction 1

    1.1 Acknowledgements 1 1.2 Introduction and explanations 1 1.3 The captive population 1 1.4 Wild Status 2 1.5 Acronyms 2 1.6 Studbook Legend 3

    2. The natural history of scimitar-horned oryx 4

    2.1 Taxonomy 4 2.2 Morphology 4 2.3 Reproduction 4 2.4 Social structure 5 2.5 Ecology 5

    3. Conservation of Scimitar-horned Oryx 7

    3.1 Current and former status 7 3.2 Conservation measures 8

    4. Research 12

    4.1 Evaluating conservation breeding success for an Extinct-in-the-Wild antelope

    12

    4.2 Fecal parasite identification by microscopy and PCR in scimitar- horned oryx, Oryx dammah, managed at two sites 4.3 Vegetative habitat selection of Scimitar horned oryx (Oryx dammah) in

    Bouhedma National Park, Southern Tunisia

    12

    13

    5. References and Bibliography 14 6. Global Management of Scimitar-horned Oryx 23

    6.1 Data currentness 6.2 Population analyses

    24 28

    6.3 Inbreeding coefficient report 30 7. Living 221 8. Births 2016 293 9. Deaths 2016 307 10. Transfers 2016 322 11. Historical Studbook 331 12. Location Glossary 863

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    1. Introduction 1.1 Acknowledgements I would like to thank all those institutions and individuals who have provided data for this studbook, and Species360 for filling in the gaps. 1.2 Introduction and explanations This is the twelfth edition of the international studbook for scimitar-horned oryx and aims to provide information on the global captive population. All individuals in the studbook that have been assigned permanent international studbook numbers should be added to institutional records. This publication contains some demographic and genetic information to inform holders of scimitar-horned oryx about the general status of the global population. However, it is not designed to supersede any analyses or breeding recommendations produced by regional coordinators. The data include all global institutions who have provided information on their collection of scimitar-horned oryx regardless of regional zoo association affiliations and membership of coordinated breeding programmes. This full register and studbook for scimitar-horned oryx updates any previously published register. 1.3 The captive population The data reported in this studbook are current through to 31 December 2016. As of that date, the historical population was 5022.4700.245 (9967) animals in 468 institutions, and the living population was 615.874.42 (1531) animals in 154 institutions. This number includes: 225.289.27 (541) animals in 29 institutions in the Asian region; 25.35.3 (63) animals in 5 institutions in the Australasian region; 13.20.4 (37) animals in 4 institutions in the Central & South American region; 155.264.7 (426) animals in 74 institutions in the European region; 147.211.0 (358) animals in 35 institutions in the North American region In 2016, there were: 115.111.11 (237) births in 52 global institutions; 69.84.12 (165) deaths in 65 global institutions; 58.47.0 (105) transfers in 37 global institutions

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    1.4 Wild Status The IUCN Red List of Threatened Species (Version 3.1) lists the scimitar-horned oryx as ‘Extinct in the Wild’ and there has been no evidence of its persistence in the wild for over 15 years. The species is listed in Appendix 1 of the Convention on Migratory Species (CMS), and in Appendix I on the Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES) (IUCN SSC Antelope Specialist Group , 2016). Further information can be found at www.iucnredlist.org.

    1.5 Acronyms ARKS Animal Record Keeping System ASMP Australasian Species Management Program AZA The Association of Zoos and Aquariums EAD The Environment Agency – Abu Dhabi EAZA European Association of Zoos and Aquaria EEP European Endangered Species Programme F Inbreeding coefficient FGE Founder Genome Equivalents GD Gene Diversity GV Gene Value ISIS International Species Information System JAZA Japanese Association of Zoos and Aquaria MK Mean Kinship NGO Non Government Organisation NP National Park PMx Population Management 2000 SCF Sahara Conservation Fund SHO Scimitar-horned oryx SPARKS Single Population Analysis and Record Keeping System SSIG Sahelo-Saharan Interest Group SSP Species Survival Plan WAZA World Association of Zoos and Aquariums ZAA Zoo and Aquarium Association ZIMS Zoological Information Management System

    http://www.iucnredlist.org/

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    1.6 Studbook legend

    Stud#: Animal's permanent studbook number. Studbook numbers may not

    always be assigned chronologically, due to animals being recorded as they become known to the Studbook Keeper.

    Sex: M for male, m for castrated male, F for female, cont if contracepted,

    neut if neutered, U for unknown sex Birth Date: Animal's birth date. A tilde mark, '~', before a date indicates that it

    is approximate. '??' indicates that the date is unknown. Sire and Dam: Studbook numbers for the animal's sire and dam. 'UNK' if unknown.

    'MULT' if several candidates have been identified. 'WILD' if the sire or dam was considered to be wildcaught - this animal is a founder.

    Location: The institution holding the animal at the time. If the animal is no

    longer traceable by the Studbook Keeper, 'ltf' (lost-to-followup) will appear to the right of the last known location.

    Date: The date on which the event occurred. A tilde mark, '~', before a

    date indicates that it is approximate. '??' indicates that the date is unknown.

    Local ID: The identification assigned by the specimen's location, often its ISIS

    number, house number, or occasionally house name. Event: Capture, Birth, Transfer, Loan, Ownership change, Death or

    Release Identifiers: House Name, Transponder, Tag/Band, Tattoo, Notch

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    2. The natural history of scimitar-horned oryx

    In this international studbook for scimitar-horned oryx, I summarise available information on the natural history and conservation of the species. For more detailed information see the ‘biology, husbandry and conservation of scimitar-horned oryx (Oryx dammah)’ published in 2004 and the papers and reports listed in the bibliography. 2.1 Taxonomy Kingdom: Animalia Phylum: Chordata Class: Mammalia Order: Artiodactyla Suborder: Ruminantia Family: Bovidae Sub-family: Hippotragini Genus: Oryx Species: Dammah Common name: Scimitar-horned oryx, scimitar oryx, Sahara oryx, oryx

    algazelle, antilope oryx, wach, begar al ouach (IUCN, 2004; Wakefield, 1995; Devillers & Devillers-Terschuren, 2003; Engel, 2004a)

    The scimitar-horned oryx was given the scientific name of Oryx dammah after it was described by Cretzschmar in 1826. However, examination of the available literature reveals that it has been also known as Oryx algazelle, Oryx tao, Oryx damma, Oryx bezoarticus, Oryx ensicornis and Oryx leucoryx (which now belongs to the Arabian oryx) (Dolan, 1973). There are four species in the genus oryx; scimitar-horned oryx (Oryx dammah), Arabian oryx (Oryx leucoryx), gemsbok (Oryx gazelle) and beisa oryx (Oryx beisa) which is further sub-divided into two sub-species; beisa oryx (Oryx beisa beisa) and the fringe-eared oryx (Oryx beisa callotis) (IUCN SSC Antelope Specialist Group, 2008). It is possible to cross breed all species of oryx with each other and with addax (Addax nasomaculatus) and the resulting hybrids are normally fertile (Engel, 2004a). 2.2 Morphology Scimitar-horned oryx are large, predominantly white antelope whose neck, shoulders and rump are stained a deep russet colour. Their faces are white with light brown stripes running down their nose, cheeks and through the eyes. Their most notable features are the long, slender scimitar-shaped horns which can grow to a length of 150cm, although the norm is approximately 90 to 115cm for an adult oryx (Newby, 1978a, 1988; Barzdo, 1982; Kingdon, 1997). There is no sexual dimorphism between the sexes, although males may be slightly larger than females (Dolan, 1966; Engel, 2004). At birth, calves are a light brown colour, with adult colouration developing at three to 12 months old (Dolan, 1966; Gill & Cave-Browne, 1988; Nishiki, 1992). 2.3 Reproduction Scimitar-horned oryx have a gestation period of between 242 to 300 days (approximately eight and a half months) and most of the time a single calf is born (Dolan, 1966; Dittrich, 1972; Anon, 1987; Newby, 1988). If a male is present during the female’s post-partum oestrus, it is possible for females to fall pregnant again

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    immediately. Therefore, under favourable conditions females can have a calf every eight and a half to nine months (Nishiki, 1992; Wakefield & Engel, 2004). As such it may be necessary to separate the sexes at certain times of the year to control breeding. Calves are capable of following their mothers a few hours after birth (Dolan, 1966), but in the wild lay hidden in vegetation for the first two weeks of their life (IUCN, 1987; Gill & Cave-Browne, 1988). After two weeks they are crèched with calves of a similar age and are weaned at four to ten months (Newby, 1974; 1984; Mayor, 1984; Gill & Cave-Brown, 1988). In captivity, the calves will be crèched in a suitable location in the enclosure. Females reach sexual maturity between 11 and 35 months, and males between 10 and 30 months (Dittrich, 1970, 1972; Dolan, 1976; Gill & Cave-Browne, 1988; Puschmann, 1989; Nishiki, 1992; Volf, 1994; Engel, 2004b). 2.4 Social structure Before their extinction in the wild, scimitar-horned typically formed herds of between 15 and 40 animals, but at certain times of the year, during their seasonal migrations or in areas of fresh pasture, aggregations of thousands could be seen (Dolan, 1966; Newby, 1978a, 1988; Barzdo, 1982, Devillers & Devillers-Terschuren, 2004). Some authors have suggested that herds were led by an adult bull (Dolan, 1966; Kranz & Ralls, 1979), but Newby (1974) reported that an adult female leads the group. Old males expelled from the herds tended to be solitary (Dolan, 1966), although it is possible that bachelor herds were formed (Engel, 2004c). Scimitar-horned oryx have a well-defined linear dominance hierarchy (Pfeifer, 1985; Engel, 2004d) which is evident in zoological institutions and at release sites in Tunisia (Wacher, 1986; Gordon, 1987; Molcanova, 2004). However, this may be disrupted if an individual is removed from the herd for some period of time and reintroduced at a later date (Engel, 2004d). The social organisation of captive scimitar-horned oryx is dictated either by the institutions in which they are held or the requirements of the regional coordinated captive breeding programme. European zoos hold all-female herds, bachelor herds, or harem groups with mixed sex calves. The majority of the herds are all-female or harem groups and this has resulted in a surplus male problem which needs addressing. 2.5 Ecology Historically scimitar-horned oryx could be found on the arid grassy steppe that lies between the Sahel and the desert vegetation zones to the south of the Sahara (Newby, 1978a), and the Mediterraneo-Saharan transition zone to the north of the Sahara (Devillers & Devillers-Terschuren, 2003). These areas are characterised by scrub vegetation, scattered trees, rolling dunes and wooded inter-dunal depressions receiving an annual rainfall of 100 to 400mm (Dolan, 1966; Newby, 1978b, 1980, 1988; Anon, 1987). The rain falls in just one season, to the south of the Sahara this is from June to September (Anon, 1987; Newby, 1988) and to the north the rains begin in September at the earliest (E.Flach, pers comm.). Shade is an important factor in modifying scimitar-horned oryx distribution, and at the hottest times of the day the oryx seek shade in wooded wadis and inter-dunal depressions to conserve water (Anon, 1987; Newby, 1988). This results in the oryx exhibiting a crepuscular activity pattern with their peak activity at dawn and dusk when they can be observed feeding (Anon, 1987; di Croce, pers. comm.). Scimitar-horned oryx are primarily grazers feeding on a wide variety of grasses and leguminous plants, but will occasionally take browse and other food resources such as the fallen seed pods of Acacia tortilis (Dolan, 1966; Anon, 1987). On fresh green pastures oryx need little drinking water as the vegetation meets their water requirements, but in the hot season scimitar-horned oryx seek out water rich plants such as the wild bitter melon Citrullus colocynthis, and will go to great lengths to

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    obtain fresh water even though they are able to go without drinking for nine or ten months of the year (Dolan, 1966; Anon, 1987; Newby 1978a, 1988). The oryx evolved a migratory response to cope with the hot season or times of drought, and in former times these great migrations in search of food and rain numbered thousands of individuals (Dolan, 1966; Newby, 1978a, 1980, 1988; Barzdo, 1982). Historically scimitar-horned oryx were subject to predation from a number of large carnivores including; cheetah Acinonyx jubatus, striped and spotted hyaena Hyaena hyaena and Crocuta crocuta respectively, wild dog Lycaon pictus and lion Panthera leo. Most predators have been exterminated from the Sahel thanks to systematic persecution (Newby, 1988) however there are reports that jackals pose a threat to oryx calves in Sidi Toui National Park, Tunisia (Molcanova, 2004).

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    3. Conservation of Scimitar-horned Oryx 3.1 Current and former status The scimitar-horned oryx (SHO) is listed as ‘Extinct in the Wild’ in the IUCN Red List of Threatened Species (IUCN SSC Antelope Specialist Group, 2016). The SHO is Sahelian in its distribution with its former range extending both north and south of the Sahara from Mauritania eastwards to Sudan, Egypt westward to Western Sahara (Dolan, 1966; Anon, 1987; Dixon et al, 1991). In the north of their range, the SHO would have been geographically constrained by the Sahara and the Mediterranean sea, and in all probability were never as numerous as the SHO population south of the Sahara (Newby, 1978a, 1988). In the east of their range, the Nile made an effective barrier against dispersal, and to the west, the Sahara runs into the Atlantic. Only to the south of the Sahara would the SHO have been unencumbered by physical barriers, and it was there that they could be found in the largest number (Newby, 1988). SHO were formerly widespread throughout the Sahelian zone but successive waves of human occupation constrained their distribution, and their numbers dramatically declined until they were classified as ‘extinct in the wild’ (Newby, 1978a, 1988; Gordon, 1991; IUCN, 2002). The trend towards extinction in the wild was faster in the Sahelian zone north of the Sahara than the southern Sahelian Zone, and the northern population of SHO were probably exterminated by 1900 (Newby, 1978a). Up until the 1920s and 1930s, SHO were abundant throughout the southern part of their range from the Atlantic to the Nile and were considered common in some areas (Anon, 1987; Newby 1978). By 1978, the largest remaining population could be found in the Ouadi Rimé-Ouadi Achim Game Reserve (OROA) in Chad. However, political unrest meant that conservation efforts in this area had to be abandoned until 1986. By mid 1987, it is almost certain that the number of SHO in the wild had plummeted to less than a 1000 with the only surviving population being found in OROA (Anon, 1987). The last SHO in Chad was reportedly killed in 1989 on the Ouadi Kharma in the OROA. It was a male and had previously been seen for a couple of years with two other animals. A survey in Chad in 2001 found no evidence of any remaining SHO in the wild (Moksia et al., 2001). Figure 1. The last known photograph of scimitar-horned oryx before their extinction in the

    wild. The photograph was taken by John Newby in Niger

    A number of factors have contributed to the decline and eventual extinction of SHO in the wild (Newby, 1988). These include; over-hunting, civil unrest, development,

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    drought, and competition with domestic livestock (Dixon et al, 1991; Wakefield, 1992; Wakefield et al., 2004). 3.2 Conservation measures SHO have been part of zoological collections since the 1890s, but most of the ex-situ population is descended from a capture of wild animals in Chad in the mid 1960s (Rost, 1985; Dixon et al., 1991). These SHO, and their offspring, were distributed to zoological institutions in Europe, North America, Japan and more recently Australasia (Dixon et al., 1991). The records of these transactions are incomplete and the ancestry of many animals is not fully known. In total, the number of wild-caught founders of the global population is estimated to be 40 – 50 (Dixon et al., 1991; Mace, 1986). On an international level, Europe (EEP), North America (SSP), and Australasia (ASMP) have co-ordinated captive breeding programmes for SHO, although there are a large number of SHO outside of formal breeding programmes, particularly on ranches in the USA and in collections in the Arabian Peninsula. The Environment Agency-Abu Dhabi have a collection of more than 3000 SHO. Tunisia A number of projects have taken place in which SHO populations have been restored to fully fenced or partially fenced protected areas. The first was in Tunisia in 1985 and involved the transfer of 10 SHO from Marwell and Edinburgh zoos, UK, to Bou Hedma National Park (NP) (Gordon, 1991). The population was augmented by additional male SHO from Bratislava zoo in 1999. The Tunisian SHO population was increased in 1999 when 10 (1.9) and 3 (1.2) SHO were sent from various EEP zoos to Sidi Toui NP and Oued Dekouk Nature Reserve (NR) respectively (Molcanova, 2003). The most recent Tunisian SHO reintroduction project began in February 2007 when eight SHO (3.5) were translocated from Bou Hedma NP to Dghoumes NP, close to Tozeur in Tunisia. In December of the same year, nine (5.4) SHO from EEP and SSP institutions were transported to the Park to genetically augment the population. The population experienced high birth rates and low mortality rates, until southern Tunisia experienced a drought in 2012 and 2013. The fauna and flora in all the southern Tunisian protected areas were affected, and the SHO population suffered from low birth rates and increased mortality. Fortunately, the rains returned at the end of 2013 and the habitats and SHO were quick to recover (Figures 2 & 3). The project in Dghoumes National Park is continuing with regular post-release monitoring, capacity building and training of eco-guards, development of an eco-museum, health monitoring of SHO populations and biodiversity surveying. Other projects on wider Sahelo-Saharan biodiversity are ongoing across several parks and reserves and include the genetic analysis of the Tunisian SHO metapopulation, the reintroduction of the North African ostrich, rescue and rehabilitation of spur-thighed tortoises trafficked for the pet trade, dorcas gazelle conservation, and monitoring of the reintroduced addax populations in Djebil and Senghar National Parks. The current Tunisian metapopulation of SHO consists of approximately 200 individuals divided across the protected areas. Please see Woodfine & Gilbert (2016) for a review of SHO conservation work in Tunisia.

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    Figure 2. SHO in Dghoumes National Park, Tunisia. Figure 3. SHO in Dghoumes National Park, Tunisia.

    Photo by Tanya Langenhorst, Marwell Photo by Robert Cooke, Marwell Wildlife Wildlife

    Figure 4. SHO in Souss Massa National Park, Figure 5. SHO in Guembeul Reserve, Senegal.

    Morocco. Photo by Heiner Engel, Erlebnis Photo by Conrad Ensenat, Barcelona Zoo Zoo

    Morocco In 1995, five SHO were reintroduced to Souss Massa NP, Morocco, and these were followed by a further two releases in 1996 and 1997. In total, 29 SHO have been sent from EEP zoos to the Moroccan National Park (Müller & Engel, 2003) and by 2011 the population had grown to ~270 individuals (Oubrou pers. comm., 2013) (Figure 4). Senegal In February 1999, Israel donated eight SHO to the Guembeul Faunal Reserve, Senegal. These were joined by four more SHO from Paris Zoo, and in January 2003 eight SHO were translocated to The Ferlo Biosphere Reserve, Senegal (Gilbert, 2004b; B. Clark pers. comm.). There are now approximately 60-70 SHO in the Ferlo Biosphere Reserve and 110-120 SHO in the Guembeul Reserve (Abaigar pers.comm., 2013) (Figure 5). Chad The largest and most recent attempt to reintroduce the SHO to its historical range is currently underway in Chad. The programme is a joint initiative between the Environment Agency-Abu Dhabi (EAD), UAE and the Government of Chad in close collaboration with the Sahara Conservation Fund (SCF) as the implementing partner

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    in Chad. A number of other global conservation organisations are contributing to the initiative. The project aims to create a healthy and self-sustaining population of 500 breeding adult SHO in the unfenced Ouadi Rimé-Ouadi Achim Game Reserve (OROA) in Chad over the next five years. OROA was the last stronghold for SHO in the wild before their extinction and extends over 77,950 km2 of Sahelian grassland and sub-Saharan habitats (Wacher et al., 2011). The source population for this reintroduction is managed by the EAD and consists of more than 3,000 individuals. The EAD has built a genetically diverse world herd by importing unrelated individuals from Europe (EEP) and North America (SSP and private holders), integrating them into the existing herd in Abu Dhabi. The European and North American SHO will breed in the UAE and their offspring may be included in future releases to Chad. On the 16th of March 2016, the first 25 SHO were transported from Abu Dhabi to the pre-release facility in OROA (Figure 6). The animals settled into the pre-release pens for a five-month acclimatisation period prior to their release into the wild. The SHO were fitted with GPS collars in July 2016, and shortly afterwards they were let out of their pens (Figure 7). They are now roaming freely within the reserve and appear to have settled into their natural habitat extremely well, finding key resources such as fresh grasses and shade (Figure 8), and have started calving with five calves being born to date in the wild (Figure 9). Second and third shipments of 25 SHO each have now arrived at the pre-release facility in OROA. Some of these (14) were released in January, 2017. The remainder will be released in August, 2017. The released SHO are being closely monitored both through the GPS collars and rangers and wildlife biologists on the ground (Figure 10). The GPS collars provide data that track and help protect individuals, but also collect movement, behavioural, life-history and ecological data on the released SHO, which can aid further species reintroduction efforts. The collars will continue to collect data for 2-3 years before remotely detaching from the oryx. The EAD and Zoological Society of London (ZSL) have also trained a team of wildlife experts and rangers in the reserve to monitor the SHO, as well as conduct community outreach programmes to ensure their continued protection. In addition to daily monitoring of SHO, the team in Chad are continuously engaging with nomadic herders who cross the protected area (Figure 11). The teams have been met with much excitement by older herders who recall the presence of SHO from their childhood. Whilst this initiative is a collaboration between the Environment Agency-Abu Dhabi, the Government of Chad and the Sahara Conservation Fund, a number of other partner organizations are contributing to this reintroduction by carrying out wildlife and habitat surveys, pre-release population modeling and genetic studies to inform release strategy, sending animals to genetically augmentation of the source population in the UAE, post-release monitoring, animal husbandry in Chad, and training and capacity building. This initiative is possibly the world’s most ambitious large mammal reintroduction programme and a huge step in the field of conservation. If you would like any further information, please visit the Environment Agency – Abu

    Dhabi website https://www.ead.ae/Pages/SHO/Index.aspx

    https://www.ead.ae/Pages/SHO/Index.aspx

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    Figure 6. First transport of SHO released into Figure 7. SHO released from the pre-release the pre-release pens in OROA. Photo into the wild in OROA. Photo by

    by Environment Agency-Abu Dhabi Sahara Conservation Fund

    Figure 8. Released SHO in OROA. Photo by John Figure 9. Second calf born in Chad. Photo by Newby, SCF the Sahara Conservation Fund

    Figure 10. Post-release monitoring of SHO. Figure 11. Nomadic herders in OROA. Photo by Photo by the Sahara Conservation Fund the Sahara Conservation Fund

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    4. Research This section provides information on some of the research that has taken place since the last publication of the international studbook for scimitar-horned oryx.

    4.1 Evaluating Conservation Breeding Success for an Extinct-in-the-Wild Antelope Holly A. Little, Tania C. Gilbert, Marie L. Athorn, Andrew R. Marshall Abstract With the number of threatened species increasing globally, conservation breeding is vitally important now more than ever. However, no previous peer-reviewed study has attempted to determine how the varying conditions across zoos have influenced breeding by an extinct-in-the-wild species. We therefore use questionnaires and studbook data to evaluate the influence of husbandry practices and enclosure design on scimitar-horned oryx (Oryx dammah) breeding success, at the herd level. Regression models were used to identify the variables that best predicted breeding success among 29 zoos across a five-year period. Calf survival decreased with herd age and the use of soft substrates in hardstand areas (yard area usually adjacent to the indoor housing), explaining 30.7% of overall variation. Calf survival also decreased where herds were small and where food provisions were not raised (and hence likely incited competition), although these were less influential. Likewise, birth rate decreased with soft substrates in hardstand areas and unraised food provisions, although these were less influential than for calf survival. Birth rate increased with year-round male presence, yet this decreased calf survival. Compared to previous studies, the number of enclosure/husbandry influences on breeding were relatively few. Nevertheless, these few enclosure/husbandry influences explained over one third of the variation in calf survival. Our data therefore suggest some potential improvements and hence that extinct-in-the-wild species stand a greater chance of survival with empirical design of zoo enclosures and husbandry methods. Citation: Little H.A., Gilbert T.C., Athorn M.L., Marshall A.R. (2016) Evaluating Conservation Breeding Success for an Extinct-in-the-Wild Antelope. PLoS ONE 11(12): e0166912. doi:10.1371/journal.pone.0166912

    The full paper is open access and available from: http://journals.plos.org/plosone/article?id=10.1371/journal.pone.0166912

    4.2 Fecal parasite identification by microscopy and PCR in scimitar-horned oryx, Oryx dammah, managed at two sites Cassandra D. Pauling, Anna R. Oller & Victoria Jackson

    Abstract

    The scimitar-horned oryx, Oryx dammah, an endangered species extinct in the wild,is managed in various captive management programs and is the focus of reintroduction efforts. Management variability can contribute to substantial parasite load differences, which can affect deworming programs and potentially transfer parasites to different regions with translocations. Parasite studies in O. dammah are lacking. In this study, we determined fecal egg/oocyst counts of O. dammah in two captive herds, Fossil Rim Wildlife Center (FRWC) and Kansas City Zoo (KCZ). Fecal egg counts (FEC) were performed on O. dammah feces collected seasonally using the modified McMaster method, and microscopy provided additional identification of parasite genera ova and oocysts. To identify parasites to species level, homogenized

    http://www.sciencedirect.com/science/article/pii/S2213224416300554http://www.sciencedirect.com/science/article/pii/S2213224416300554http://www.sciencedirect.com/science/article/pii/S2213224416300554

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    fecals provided DNA subjected to the polymerase chain reaction (PCR) using genus specific primers. Microscopy and sequencing results indicated the presence of Strongylus (Strongylus vulgaris, Angiostrongylus cantonensis), Trichostrongylus (Haemonchus contortus, Camelostrongylus mentulatus), Trichuris (T. leporis, T. ovis, and T. discolor), Isospora (Isospora gryphoni) and Eimeria (E. zuernii and E. bovis), with Strongylus being the most common. Nematodirus was identified through microscopy at FRWC. Fecal egg counts were significantly higher in (FRWC) than in (KCZ) in all samplings (P =

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    5. References and Bibliography Allen, J.L. (1996) A comparison of nalmefene and naltrexone for the prevention of

    renarcotization following carfentanil immobilization of nondomestic ungulates. Journal of Zoo and Wildlife Medicine 27: 496 - 500

    Alyousif, M.S. & Al-Shawa, Y.R. (2002) A new coccidian parasite (Apicomplexa: Eimeriidae) from the scimitar-horned oryx, Oryx dammah. Journal of the Egyptian Society of Parasitology 32: 241-246

    Anon (1987): Scimitar-horned oryx Oryx dammah. WCMC. IUCN. Unpublished report.

    Arif, I. A.; Khan, H. A.; Bahkali, A.H., Al Homaidan, A.A.); Al Farhan, A.H., Shobrak, M. & Al Sadoon, M. (2011) Comparison of neighbor-joining and maximum-parsimony methods for molecular phylogeny of oryx species using 12s rRNA and 16s rRNA gene sequences. In: Animal Science and Issues. Nova Science Publishers, Hauppauge, NY: 117-125

    Ballou, J. & Ralls, J. (1982) Inbreeding and juvenile mortality in small populations of ungulates - a detailed analysis. Biological Conservation 24: 239-272

    Barzdo, J. (1982): New hope for the scimitar. Country Life May 27: 1552 - 1553 Bassett, T.H. (1975) Oryx and addax in Chad. Oryx 13: 50-51 Bauwens, L., Vercammen, M.L.T.F. & De Meurichy, W. (2001) Occurrence of Listeria

    spp. in captive antelope herds and their environment. Journal of Zoo and Wildlife Medicine 32: 514 - 518

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    Schiewe, M.C., Bush, M., Phillips, L.G., Citino, S. & Wildt, D.E. (1991) Comparative aspects of estrus synchronization, ovulation induction, and embryo cryopreservation in the scimitar-horned oryx, bongo, eland, and greater kudu. Journal of Experimental Zoology 258: 75-88

    http://www.sciencedirect.com/science/article/pii/S2213224416300554http://www.sciencedirect.com/science/article/pii/S2213224416300554http://www.sciencedirect.com/science/journal/22132244

  • 21

    Schiewe, M.C., Bush, M., Phillips, L.G. & Wildt, D.E. (1988) Application of embryo techniques to an endangered species - the scimitar-horned oryx. Theriogenology 29: 303-303

    Shaw, H.J., Green, D.I., Sainsbury, A.W. & Holt, W.V. (1995) Monitoring ovarian-function in scimitar-horned oryx (Oryx dammah) by measurement of fecal 20-alpha-progestagen metabolites. Zoo Biology 14: 239 - 250

    Spevak, E., Gilbert, T., Engel, H. Correll, T. & Houston, B. (2006) Returning the Addax and the Oryx to Tunisia. Communiqué of the American Association of Zoos and Aquaria. April 2006: 13 – 14.

    Van Niekerk, G. (2011). Burchell golden oryx. From prince of the Kalahari to king of South Africa. African outfitter. http://www.burchellgoldenoryx.com/golden%20oryx%20AFRICAN%20OUTFITTER%20ARTICLE.pdf. Downloaded on 15 April 2015.

    Volf, J. (1994) Contribution to a comparison of the reproduction biology in three antelope species of the subfamily Hippotraginae in captivity. Zoologische Garten 64: 349-356

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    Woodfine, T. & Gilbert, T. (2016) The fall and rise of the scimitar-horned oryx: a case study of ex-situ conservation and reintroduction in practice. In: Antelope Conservation in the 21st Century: From Diagnosis to Action (Eds. J.Brø-Jorgensen and D.Mallon). Wiley & Sons, Chichester.

    Woodfine, T., Gilbert, T. & Engel, H. (2005) A summary of past and present initiatives for the conservation and reintroduction of addax and scimitar-horned oryx in North Africa: 208 – 211. In: B.Hiddinga (Ed.) Proceedings of the EAZA conference 2004, Kolmarden. EAZA Executive Office, Amsterdam.

    Woodfine, T, Petretto, M. & Gilbert, T. (2014) Conservation of scimitar-horned oryx & their arid steppe habitat in Tunisia: A report for the scimitar-horned oryx EEP. Marwell Wildlife, U.K.

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    Wacher, T., Newby, J, Bourtchiakbe, S, and Banlongar, F. (2010) Wildlife survey of the Ouadi Rimé- Ouadi Achim Game Reserve, Chad (Part I). SCF/Pan Saharan Wildlife Survey. Technical Report No. 5. March 2011, vi+ 79 pp. Sahara Conservation Fund.

    Wakefield, S. (1995): Scimitar-horned oryx Oryx dammah European studbook number 1. Marwell Preservation Trust. Unpublished report.

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    Wakefield, S., Engel, J. & Gilbert, T. (2004): Conservation. In: The biology, husbandry and conservation of scimitar-horned oryx (Oryx dammah) (T. Gilbert & T. Woodfine, Eds.). Marwell Preservation Trust, UK: 14 – 20.

    Wilson, R.T. (1980) Wildlife in Northern Darfur, Sudan - review of its distribution and status in the recent past and at present. Biological Conservation 17: 85-101

    Woodfine, T., Zahzah, K., Chetoui, A., Gilbert, T. & d’Alterio, G.L. (2009): Reintroduction of scimitar-horned oryx to Dghoumes National Park, Tunisia. Report prepared for Direction Générale des Forêts, Tunis. Marwell Wildlife, UK.

    Woodfine, T., Chetoui, A., Zahzah, K. & Gilbert, T. (2011) Re-introduction of scimitar-horned oryx to Dghoumes National Park, Tunisia. In: Global re-introduction perspectives: 2011. More case studies from around the globe. IUCN/SSC Re-introduction Specialist Group & Environment Agency; Abu Dhabi: 190- 193

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  • 22

    Zhang, H.H., Ren, Y., Chen, L. & Sha, W.L. (2012) The complete mitochondrial genome of scimitar-horned oryx (Oryx dammah). Mitochondrial DNA 23 (5): 361 - 362

  • 23

    6. Global Management of Scimitar-horned Oryx Scimitar-horned oryx are managed in three coordinated captive breeding programmes in the North American region, European region, and Australasian region. Management in the Japanese region is carried out by the regional studbook holder. In Europe and North America the management of the breeding programmes are assisted by the TAGs and elected advisors. Below are the contact details for the regional coordinators, studbook keepers and TAG chairs involved in the management of scimitar-horned oryx:

    European EEP North American SSP Tania Gilbert RoxAnna Breitigan Scimitar-horned oryx EEP coordinator Scimitar-horned oryx SSP coordinator Marwell Wildlife The Living Desert Colden Common, Winchester 47900 Portola Avenue Hampshire, SO21 1JH, UK Palm Desert, CA 92260, USA E:[email protected] E: [email protected] Japanese JAZA programme Australasian ASMP Tsunenori Tsujimoto Denny Burgoyne Scimitar-horned oryx JAZA studbook keeper Werribbe Open Range Zoo Morioka Zoological Park K Road Shimoyagaida 60-18 Werribee Shinjo, Morioka-shi, Morelia, Japan Victoria 3030, Australia E: [email protected] North American antelope and giraffe taxon advisory group: Chair Vice-chair Aridland Antelope Martha Fischer Adam Eyres Saint Louis Zoological Park Fossil Rim Wildlife Center 1 Government Drive 2299 County Road 2008 Saint Louis, MO 63110-1395, USA Glen Rose, Texas 76043, USA E: [email protected] E: [email protected] European antelope and giraffid taxon advisory group: Chair Vice-chair Vice-chair Jens-Ove Heckel Kim Skalborg Simonsen Sander Hofman Zoo Landau in der Pfalz Givskud Zoo - Zootopia Royal Zoological Society of Antwerp Hindenburgstr. 12 Løveparkvej 3, Givskud Koningin Astridplein 26 D-76829 Landau in der Pfalz DK-7323 Give 2018 Antwerpen Germany Denmark Belgium E:[email protected] E: [email protected] E: [email protected]

    mailto:[email protected]:[email protected]:[email protected]:[email protected]:[email protected]:[email protected]:[email protected]

  • 24

    6.1 Data currentness Institutions that provided 2016 data to the international studbook

    Mnemonic Institution Country 2016 Data

    AALBORG Aalborg Zoo Denmark Yes

    AL AIN Al Ain Zoo UAE Yes

    ALBG Al Bustan Gazelle Farm UAE No

    ALBUSTAN Al Bustan Zoological Center UAE Yes

    ALDERGROV Greater Vancouver Zoo Canada Yes

    ALTINA Altina Wildlife Park Australia No

    AMERSFOOR Dierenpark Amersfoort Netherlands Yes

    AMSTERDAM Artis Zoo Netherlands Yes

    ASHLANDNE Lee Simmons Conservation Park and Safari USA ZIMS

    ATTICAZOO Attica Zoological Park S A Greece Yes

    AUSTIN SA Austin Savannah (Bob Gregory) USA No

    AYWAILLE Monde Sauvage Safari Sprl, Belgium Yes

    BADOCA PK Badoca Safari Park Portugal Yes

    BAMBERGER Bamberger Ranch USA No

    BARCELONA Parc Zoologic De Barcelona Spain Yes

    BATUSECRE Batu Secret Zoo Indonesia ZIMS

    BEIJING Beijing Zoo China Yes

    BER SHEVA Negev Zoo Israel No

    BERLINZOO Zoologischer Garten Berlin Ag Germany Yes

    BERRY JIM Pony Creek Ranch (Jim Berry) USA No

    BOGOR Taman Safari Indonesia No

    BOISSIERE Espace Zoologique La Boissiere Du Dore France Yes

    BORYSEW Zoo Safari Borysew Poland No

    BOUILLON Bouillon Belgium ZIMS

    BREVARD Brevard Zoo USA Yes

    BRIGHTSFA Bright’s Zoo USA ZIMS

    BURFORD Cotswold Wildlife Park and Gardens UK Yes

    BUSCH TAM Busch Gardens USA Yes

    BUSSOLENG Parco Natura Viva Italy ZIMS

    CAIRO ZOO Cairo Zoo Egypt Yes

    CAPE MAY Cape May Zoo USA Yes

    CHAMPREP Parc Zoologique de Champrepus France Yes

    CHESINGTN Chessington World of Adventures Ltd UK Yes

    CHESTER North of England Zoological Society UK Yes

    CHIBA SHI Chiba Zoological Park Japan Yes

    COLOMBO National Zoological Gardens Sri Lanka ZIMS

    DAEJEON Bomunsan Daejeon Zoo Republic of Korea No

    DALLAS Dallas Zoo USA ZIMS

    DEBRECEN Nagyerdei Kult·rpark Kht Hungary ZIMS

    DELEIKA Deleika Wildlife Conservation Center UAE ZIMS

    DISNEY AK Disney's Animal Kingdom USA Yes

    DUBAI ZOO Dubai Zoo UAE Yes

    DUBBO Taronga Western Plains Zoo Australia ZIMS

    DUBLIN Zoological Society of Ireland-Dublin Ireland Yes

    DVOREC Zoo Dvorec Czech Republic Yes

  • 25

    Mnemonic Institution Country 2016 Data

    DVUR KRALV Dvur Kralove Zoo Czech Republic Yes

    ELCHE SAF Rio Safari Elche Spain No

    ESTEPONA Parque De La Naturaleza Selwo (grpr) Spain No

    FALCONARA Parco Zoo Di Falconara Italy Yes

    FASANO Zoosafari Fasano Italy Yes

    FOSSIL RIM Fossil Rim Wildlife Center USA Yes

    FOTA Fota Wildlife Park Ireland Yes

    FREJUS Parc Zoologique de Fréjus France No

    FRIGUIA Fruigia Zoo Tunisia No

    GDANSK Miejski Ogrod Zoologiczny Wybrzeza Poland ZIMS

    GUADALJR Guadalajara Zoo Mexico ZIMS

    GUAT CITY Guat City Zoo Guatamala ZIMS

    GUERNO Parc Zoologique De Chateau De Branféré France Yes

    HAI KEFF Hai-Keff Zoo Israel Yes

    HAUGALAND Haugaland Zoo Norway No

    HEMMINGFD Parc Safari Canada ZIMS

    HODENHGN Serengeti-Park Hodenhagen Germany ZIMS

    HODONIN Zoo Hodonin Czech Republic Yes

    JACKS TWP Siz Flags Great Adventure USA Yes

    JERUSALEM The Tisch Family Zoological Gardens Israel Yes

    JOHANSBRG Johannesburg Zoological Gardens South Africa ZIMS

    JURQUES Parc Zoologique De Jurques France Yes

    KAMO GUN Izu Animal Kingdom (Gio Park) Japan No

    KANSASCTY Kansas City Zoo USA Yes

    KARLSRUHE Zoologischer Garten Karlsruhe Germany Yes

    KATOWICE Silesian Zoological Garden Poland Yes

    KHORAT Nakhon Ratchasema Zool. Park Thailand ZIMS

    KNOWSLEY Knowsley Safari Park UK Yes

    KOSICE Zoologicka Zahrada Kosice Slovakia ZIMS

    KREFELD Zoo Krefeld GmbH Germany Yes

    KYIV Kyiv Zoo Ukraine No

    LA PALMYR Parc Zoologique De La Palmyre France Yes

    LA TESTE Zooland Park France Yes

    LAMONGAN Maharani Zoo & Goa Indonesia ZIMS

    LE PAL Parc Zoologique De Pal France Yes

    LE VIGEN Parc Paysager et Animalier du Reynou France Yes

    LEIPZIG Zoologischer Garten Leipzig Germany Yes

    LEON Patronato Del Parque Zoologico De Leon Mexico ZIMS

    LISBON Jardim Zoologico / Lisbon Zoo Portugal Yes

    LISIEUX Z Cerza Centre D'Etude Rech Zool Augeron France Yes

    LODZ Miejski Ogrod Zoologiczny W Lodz Poland Yes

    LONGLEAT Longleat Safari & Adventure Park UK Yes

    LOWRY Tampa's Lowry Park Zoo USA No

    LVZOO Leigh Valley Zoo USA ZIMS

    MALTON Flamingo Land Ltd UK Yes

    MANOR HS Manor House Wildlife Park UK ZIMS

    MARWELL Marwell Wildlife UK Yes

  • 26

    Mnemonic Institution Country 2016 Data

    MEMPHIS Memphis Zoo USA Yes

    MEXICOCTY Zoologico de Chapultepec Mexico ZIMS

    MICANOPY Micanopy Zoological Preserve USA No

    MONARTO Monarto Zoo Australia Yes

    MONTPELLI Parc De Lunaret France Yes

    MURES ZOO Gradina Zoologica Tirgu-Mures Romania No

    NIGHTSAF Chiangmai Night Safari (dasta) Thailand No

    NISHIMURO Nanki Shiraham Adventure World Japan No

    NZP-CRC NZP-Conservation Research Center USA Yes

    NZP-WASH Smithsonian National Zoological Park USA Yes

    OBTERRE Parc De La Haute-Touche (mnhn) France ZIMS

    ODAN Odejewski-Odan Sp. Zoo Poland Yes

    OLMENSE Olmense Zoo Belgium ZIMS

    OPOLE Ogrod Zoologiczny Opole Poland ZIMS

    ORANA Orana Wildlife Park New Zealand Yes

    PARIS ZOO Paris Zoo France ZIMS

    PELISSANE Zoo De La Barben (pelissane) France Yes

    PLAISANCE African Safari France Yes

    PLANCKNDL Wild Animal Park Mechelen Planckendael Belgium Yes

    PLOCK Miejski Ogrod Zoologiczny Plock Poland Yes

    POMBIA Safari Park Italy No

    PRAHA Zoological Garden Prague Czech Republic Yes

    PRETORIA National Zoological Gardens of South Africa South Africa ZIMS

    PT ST PER Planete Sauvage France Yes

    PUNTAVERD Parco Zoo Punta Verde Italy Yes

    RAMAT GAN Zoological Center Tel Aviv Israel ZIMS

    RHINOLION Rhino and Lion Nature Reserve South Africa No

    RICHMOND King Animaland Park USA No

    ROLLING H Rolling Hills USA ZIMS

    SAFARI W Safari West USA Yes

    SAN FRAN San Francisco Zoo USA Yes

    SDWAP San Diego Wild Animal Park USA Yes

    SEOUL Seoul Grand Park Zoo South Korea ZIMS

    SHANGHAI Shanghai Zoo China No

    SINGAPORE Singapore Zoological Gardens Singapore ZIMS

    SOFIAZOO Sofia Zoo Bulgaria ZIMS

    SOUTHWICK Southwick Zoo USA ZIMS

    STATEN IS Staten Island Zoo USA ZIMS

    STUTTGART Wilhelma Zoo Germany ZIMS

    THOIRY Thoiry Zoological Park France Yes

    TOBE Ehime Prefectural Tobe Zoo Japan Yes

    TOKYOTAMA Tama Zoological Park Japan Yes

    UTICA Utica Zoo USA No

    VA SAFARI Virginia Safari Park and Preserve USA ZIMS

    VALBREMBO Parco Faunistico Le Cornelle S R L Italy Yes

    VALCORBA Parco Faunistico Valcorba Italy ZIMS

    VINPEARL Vinpearl Safari and Conservation Park Vietnam ZIMS

  • 27

    Mnemonic Institution Country 2016 Data

    W PALM BE Lion Country Safari USA Yes

    WARSAW Miejski Ogrod Zoologiczny Warsaw Poland Yes

    WERRIBEE Werribee Open Range Zoo Australia Yes

    WHIPSNADE ZSL Whipsnade Zoo UK Yes

    WILD WRLD Wildlife World Zoo USA ZIMS

    WILDS The Wilds USA Yes

    WINSTON Wildlife Safari Inc USA ZIMS

    WOBURNLTD Woburn Safari Park UK Yes

    WROCLAW Zoo Wroclaw Sp Z O O Poland Yes

    ZAGREB Zagreb Zoo / Zooloski Vrt Zagreb Croatia ZIMS

    ZAMOSCZSM Ogrod Zoologiczny Im Stefana Milera Poland ZIMS

    ZOO KOKI Zoo Koki Spain Yes

    ZOOSAFARI Zoo Safar Swierkocin Poland No

  • 28

    6.2 Population analyses

    Figure 12. Age pyramid for the global population of scimitar-horned oryx living on the 31st December

    2016

    Figure 13. Census 1950 to present for the global scimitar-horned oryx population

  • 29

    Figure 14. Fertility (Mx) throughout the age classes Figure 15. Survivorship (Lx) throughout the age

    for the global population (smoothed x2) classes for the global population. (smoothed x2)

    Figure 16. Age specific mortality (Qx) for the Figure 17. Age specific reproductive value (Vx)

    global population (smoothed x2) for the global population (smoothed x2)

    Table 1. Population statistics for the global population of scimitar-horned oryx

    Demographic Summary Genetic Summary

    Life expectancy 9.8 years Founders 62 30 day mortality 17% Living animals 1553 Oldest living 26.2 years Living descendants 747.53 Growth rate (λ) 1.110 % ancestry known 48% Growth rate (r) 0.104 % ancestry certain 33% R0 1.857 Mean inbreeding* 0.1134 Generation length (T) 5.9 years Ne/N 0.2793

    * The mean inbreeding is calculated from those individuals with known ancestry and therefore only represents part of the population

  • 6.3 Inbreeding coefficient report Studbook # Sex Age (y) Location % known % certain F

    30

    4964 M

    PHILADELP 0 0 0

    4968 F 10 PHILADELP 0 0 0

    4972 M

    PHILADELP 0 0 0

    4976 F 0 PHILADELP 0 0 ???

    4980 M 7 PHILADELP 0 0 ???

    4984 F 0 PHILADELP 0 0 ???

    4988 F 4 PHILADELP 0 0 0

    4992 M

    PHILADELP 0 0 0

    4996 F

    PHILADELP 0 0 0

    5000 M

    SYDNEY 0 0 0

    5004 M

    PARIS ZOO 1 1 0

    5008 F

    PARIS ZOO 1 1 0

    5012 F

    PARIS ZOO 1 0.5 0

    5016 M

    PARIS ZOO 1 1 0

    5020 F

    PARIS ZOO 1 1 0

    5024 M 17 ANTWERP 1 0.5 0.0833

    5028 M 10 PARIS ZOO 1 0.75 0.25

    5032 F 10 PARIS ZOO 1 0.75 0.25

    5036 F 7 PARIS ZOO 1 0.75 0.25

    5040 F 6 PARIS ZOO 1 0.375 0.1667

    5044 F 2 PARIS ZOO 0.5 0.375 ???

    5048 M 1 ZURICH 0.5 0.375 ???

    5052 F 1 ZURICH 0.5 0.375 ???

    5056 M

    UNKNOWN 0 0 0

    5060 M

    CAIRO ZOO 1 1 0

    5064 F

    CAIRO ZOO 1 1 0

    5068 F

    CAIRO ZOO 1 1 0

    5072 M 0 PARIS ZOO 0.5 0.375 ???

    5076 F 12 ANTWERP 1 0.375 0.2743

    5080 F 0 PARIS ZOO 0.5 0.375 ???

    5084 M 7 BERLINZOO 1 0.5 0

    5088 F 3 HAMBURG 1 0.5 0

    5092 F 2 CHICAGOBR 0 0 0

    5096 F 8 CHICAGOBR 0 0 0

    5100 M 14 CHICAGOBR 0 0 0

    5104 Unk 0 PARIS ZOO 0.5 0.375 ???

    5108 M 13 ANTWERP 0.5 0.375 ???

    5112 M 1 PARIS ZOO 0.5 0.375 ???

    5116 M 16 HAMBURG 0 0 0

    5120 F 16 ANTWERP 1 0.4375 0.2364

    5124 M 0 ANTWERP 1 0.4375 0.2364

    5128 M 6 CAIRO ZOO 1 0 0.0625

    5132 F 8 BERLINZOO 1 0 0.1146

    5136 F

    PARIS ZOO 1 1 0

    5140 M 22 PARIS ZOO 1 0.4375 0.2364

    5144 F 9 PARIS ZOO 1 0.4688 0.389

    5148 F 12 HANNOVER 1 0.5 0

    5152 F 3 CHICAGOBR 0 0 ???

    5154 M

    PARIS ZOO 0 0 0

  • Studbook # Sex Age (y) Location % known % certain F

    31

    5156 M 4 ANTWERP 1 0.4375 0.2364

    5160 Unk 0 ANTWERP 1 0.4688 0.389

    5164 F 1 CHICAGOBR 0 0 ???

    5168 F 18 PARIS ZOO 0.75 0.1875 0.1883

    5172 F 1 CHICAGOBR 0 0 ???

    5176 F 0 BERLINZOO 1 0.25 0.2604

    5180 F 0 CHICAGOBR 0 0 ???

    5184 M 0 PARIS ZOO 0 0 0

    5188 F 2 CAIRO ZOO 1 0 0.1224

    5192 F 0 PARIS ZOO 0 0 0

    5196 F 0 PARIS ZOO 0 0 0

    5200 F 4 BERLINZOO 1 0.25 0.2604

    5204 M 0 ANTWERP 0.75 0.4063 0.3602

    5208 M 0 ANTWERP 0.75 0.375 0.4497

    5212 M 7 BERLINZOO 0.9875 0.2188 0.1751

    5216 F 0 PARIS ZOO 0.5 0.2188 ???

    5220 F 3 AMSTERDAM 0.9688 0.2188 0.1855

    5224 M

    AALBORG 1 1 0

    5228 F

    AALBORG 1 1 0

    5232 F

    AALBORG 1 1 0

    5236 M

    AALBORG 1 1 0

    5240 F

    AALBORG 1 1 0

    5244 F

    AALBORG 1 1 0

    5248 F

    AALBORG 1 1 0

    5252 F

    AALBORG 1 1 0

    5256 F

    AALBORG 1 1 0

    5260 M 0 NAPLES 0.75 0.4063 0.3602

    5264 F 0 CAIRO ZOO 1 0 0.1339

    5268 M 11 KOLN 0.75 0.375 0.4497

    5272 M 1 BARCELONA 0.5 0.2188 ???

    5276 M 10 AMSTERDAM 0.9688 0.2188 0.1855

    5280 F 8 CATSKILL 1 1 0

    5284 F 0 BARCELONA 0.5 0.2188 ???

    5288 F 0 ANTWERP 0.75 0.375 0.4497

    5292 M 0 WULFF W 0.75 0.4063 0.3602

    5296 M 19 CATSKILL 1 1 0

    5300 F 10 L RUHE 1 1 0

    5304 F 7 BARCELONA 0.5 0.2188 ???

    5308 F 13 PARIS ZOO 0.9719 0.2188 0.2313

    5312 M 7 HANNOVER 0.9938 0.1094 0

    5316 M 0 BERLINZOO 0.9938 0.2344 0

    5320 M 0 BARCELONA 0.5 0.2188 ???

    5324 F 3 CATSKILL 1 1 0

    5328 F 12 SAN ANTON 1 1 0

    5332 F 0 PARIS ZOO 0 0 0

    5336 F 0 ANTWERP 0.75 0.4063 0.3602

    5340 M 0 BERLINZOO 0.9938 0.2344 0

    5344 F 0 BERLINZOO 0.9938 0.2344 0

    5348 F 19 SAN ANTON 1 1 0

    5352 F 12 SAN ANTON 1 1 0

    5356 M 23 NZP-WASH 1 1 0

    5360 F 19 NZP-WASH 1 1 0

  • Studbook # Sex Age (y) Location % known % certain F

    32

    5364 F 2 AMSTERDAM 0 0 0

    5368 M 1 ANTWERP 0 0 0

    5372 M 11 ANTWERP 0 0 0

    5376 M 3 SOEST 1 1 0

    5380 F 17 NZP-WASH 1 1 0

    5384 F 2 SAN ANTON 1 1 0

    5388 F 22 SAN ANTON 1 1 0

    5392 F 15 SAN ANTON 1 1 0

    5396 M

    TOKYOTAMA 1 1 0

    5400 M

    PRETORIA 0.9969 0.5547 0

    5404 M 5 PELISSANE 0.5 0.2188 ???

    5408 F 5 PELISSANE 0.9536 0.2188 0.2235

    5412 M 0 CAIRO ZOO 0.9969 0.5547 0

    5416 F 0 AMSTERDAM 0.4844 0.1094 ???

    5420 F 1 CATSKILL 1 1 0

    5424 F 18 CATSKILL 1 1 0

    5428 M 7 SAN ANTON 1 1 0

    5432 M 12 SAN ANTON 1 1 0

    5436 F 22 SAN ANTON 1 1 0

    5440 F 18 SAN ANTON 1 1 0

    5444 M 13 LOSANGELE 1 1 0

    5448 F 12 LOSANGELE 1 1 0

    5452 F 17 SANDIEGOZ 1 1 0

    5456 F 2 MEMPHIS 1 1 0

    5460 F 16 MEMPHIS 1 1 0

    5464 F 17 MEMPHIS 1 1 0

    5468 M 16 OMAHA 1 1 0

    5472 F 17 OMAHA 1 1 0

    5476 F 4 OMAHA 1 1 0

    5480 F

    AMSTERDAM 1 1 0

    5484 M

    HOLIDAY 0 0 0

    5488 F 0 PARIS ZOO 0.5 0.2188 ???

    5492 F 0 PARIS ZOO 0.5 0.2188 ???

    5496 M 0 CATSKILL 1 1 0

    5500 M 3 ANTWERP 0.5 0.2188 ???

    5504 F 0 PARIS ZOO 0.5 0.2188 ???

    5508 F 5 L RUHE 0.9969 0.5547 0

    5512 F

    TOKYOTAMA 1 1 0

    5516 M 0 PARIS ZOO 0.5 0.2188 ???

    5520 M 17 SANDIEGOZ 1 1 0

    5524 F 17 SANDIEGOZ 1 1 0

    5528 M 17 CATSKILL 1 1 0

    5532 F 9 AMSTERDAM 1 1 0

    5533 F

    PRETORIA 1 1 0

    5534 F

    PRETORIA 1 1 0

    5536 M 10 PENROSE 1 1 0

    5540 M 1 BARCELONA 0 0 0

    5544 M 0 GELSNKRKN 0.9969 0.5547 0

    5548 F

    PRAHA 1 1 0

    5552 F

    PRAHA 1 1 0

    5556 M 4 MONTPELLI 0 0 0

    5560 M

    PRAHA 1 1 0

  • Studbook # Sex Age (y) Location % known % certain F

    33

    5564 M 0 CATSKILL 1 1 0

    5568 M 9 DOSWELL 0 0 0

    5572 F

    HANNOVER 1 1 0

    5576 F 11 HAI BAR 0 0 0

    5580 M

    BREMERHVN 0.955 0 0.0256

    5584 F

    BREMERHVN 0.9494 0 0.028

    5588 M

    PRAHA 0 0 0

    5592 M

    BERLIN TP 1 1 0

    5596 F

    BERLIN TP 1 1 0

    5600 F 0 AMSTERDAM 0.9844 0.6094 0

    5604 M 1 FERNDALE 1 1 0

    5608 M 2 AMSTERDAM 1 1 0

    5612 M 11 HITACHI 1 1 0

    5616 M 0 EDMONTON 1 1 0

    5620 M 0 EDMONTON 1 1 0

    5652 M 0 EDMONTON 1 1 0

    5656 M 0 EDMONTON 1 1 0

    5660 F 1 MALLORCA 0.9969 0.5547 0

    5664 F 36 BUSCH TAM 1 1 0

    5668 F 19 BULVERDE 1 1 0

    5672 F 0 CATSKILL 0.5 0.5 ???

    5676 F 0 CATSKILL 0.5 0.5 ???

    5680 M

    MARWELL 1 1 0

    5684 M 4 HAI BAR 1 1 0

    5688 F 10 MARWELL 1 1 0

    5692 F 5 MARWELL 1 1 0

    5696 F 5 MARWELL 1 1 0

    5700 F 4 MARWELL 1 1 0

    5704 F

    MARWELL 1 1 0

    5716 M

    BERLIN TP 0.9747 0 0.0381

    5720 F

    BERLIN TP 1 1 0

    5724 F 13 FERNDALE 1 1 0

    5728 M 0 AMSTERDAM 0.9844 0.6094 0

    5732 F 1 NZP-WASH 1 1 0

    5736 M 16 UNKNOWN 1 1 0

    5740 F 13 FERNDALE 1 1 0

    5744 M 16 UNKNOWN 1 1 0

    5748 F 15 SAN ANTON 1 1 0

    5752 M 16 UNKNOWN 1 1 0

    5756 M 1 MECOM R 1 1 0

    5760 M 4 BUSCH TAM 1 1 0

    5764 F 5 TOKYOTAMA 1 1 0

    5768 F 7 ANIMALES 1 1 0

    5772 M 7 ANIMALES 1 1 0

    5776 F 1 AMSTERDAM 0.9844 0.6094 0

    5780 F 3 MARWELL 1 1 0

    5784 M 0 PARIS ZOO 0 0 0

    5788 M 1 PARIS ZOO 0 0 0

    5792 M 8 AMSTERDAM 1 1 0

    5796 M 2 MOORMAN 1 1 0

    5800 M 0 HANNOVER 0.9969 0.5547 0

    5804 Unk 0 AMSTERDAM 0.9844 0.6094 0

  • Studbook # Sex Age (y) Location % known % certain F

    34

    5808 F 0 ZEEHANDLR 0.9953 0.332 0.25

    5812 F 0 ZEEHANDLR 0.9969 0.5547 0

    5816 M 1 MOORMAN 1 1 0

    5820 M 0 FERNDALE 1 1 0

    5824 F

    AFRICAN 1 1 0

    5828 M 12 STRAFFORD 1 1 0

    5832 M 0 CATSKILL 0.5 0.5 ???

    5836 M 2 MARWELL 1 0 0

    5840 M 12 MARWELL 0.9632 0 0.0091

    5844 M 9 PRETORIA 0.955 0 0

    5848 F 16 MARWELL 0.955 0 0

    5852 F 20 MARWELL 0.955 0 0

    5856 M

    AFRICAN 1 1 0

    5860 M

    HAI BAR 0.9148 0 0.0247

    5864 M

    HAI BAR 0.8758 0 0.0191

    5868 F

    HAI BAR 0 0 0

    5872 M

    LE PAL 1 0 0.187

    5876 M

    LE PAL 1 0 0.187

    5880 F

    HAI BAR 0 0 0

    5884 M

    SOEST 0.9129 0 0.022

    5889 M

    HAVANA NZ 0 0 0

    5890 F

    HAVANA NZ 0 0 0

    5892 F 0 NZP-WASH 1 1 0

    5896 M 2 L RUHE 1 1 0

    5900 M 11 HAI BAR 0 0 0

    5904 M 2 MT CARMEL 1 1 0

    5908 F 17 TOKYOTAMA 1 1 0

    5912 M 2 PARIS ZOO 1 1 0

    5916 M 15 PARIS ZOO 1 1 0

    5920 M 0 FERNDALE 1 1 0

    5924 M 15 ZEEHANDLR 1 1 0

    5928 F 18 SAN ANTON 1 1 0

    5932 M 15 ZEEHANDLR 1 1 0

    5936 M 10 HOLIDAY 1 1 0

    5940 M 0 ZEEHANDLR 1 1 0

    5944 M 0 ZEEHANDLR 1 1 0

    5948 F 9 PRAHA 1 1 0.125

    5952 F 24 OMAHA 1 1 0

    5956 M 6 KRECHTING 1 1 0.125

    5960 F 0 AMSTERDAM 0.9844 0.6094 0

    5964 M 3 ANIMALES 1 1 0

    5968 F 17 SAN ANTON 1 1 0

    5972 M 15 OMAHA 1 1 0

    5976 M 0 AMSTERDAM 0.9844 0.6094 0

    5980 F

    YO RANCH 1 1 0

    5984 F 9 PUEBLA 1 1 0

    5988 F 14 SD-WAP 1 1 0

    5992 M 1 ZEEHANDLR 1 1 0

    5996 F 0 NZP-WASH 1 1 0

    6000 F 14 MONROE 1 1 0

    6004 F 0 PRAHA 1 1 0.125

    6008 M 1 ZEEHANDLR 1 1 0

  • Studbook # Sex Age (y) Location % known % certain F

    35

    6012 M 0 YO RANCH 1 1 0

    6016 M 0 CATSKILL 0 0 0

    6020 M 0 CATSKILL 0 0 0

    6024 F 0 CATSKILL 0 0 0

    6028 M 4 CZECH REP 0 0 0

    6032 F 1 MARWELL 0 0 0

    6036 F 17 TOKYOTAMA 1 1 0

    6040 F 0 ANIMALES 1 1 0

    6044 M 0 ANIMALES 1 1 0

    6048 F 1 PRAHA 1 1 0.125

    6052 F 6 HAI BAR 1 1 0

    6056 M 0 AMSTERDAM 0.4922 0.3047 ???

    6060 F 0 LOSANGELE 1 1 0.25

    6064 F 0 LOSANGELE 1 1 0.25

    6068 F 20 SD-WAP 1 1 0

    6072 F 20 AMSTERDAM 0.9883 0.5 0.064

    6076 M 0 OMAHA 1 1 0

    6080 F 0 EDMONTON 1 1 0

    6084 M

    SOEST 1 1 0.125

    6088 M 0 ANIMALES 1 1 0.125

    6092 M

    SOEST 1 1 0.125

    6096 F 9 ACREMAN 1 0.5 0.125

    6104 F 19 MARWELL 1 1 0

    6110 M 10 MT ULLA 1 0.5 0.125

    6112 M 0 HANNOVER 0.9984 0.7773 0

    6116 M

    HAI BAR 1 1 0

    6120 F 14 MARWELL 1 0 0

    6124 M 8 UNKNOWN 1 1 0

    6128 F 17 SAN ANTON 1 1 0

    6132 F 16 PRAHA 1 1 0.125

    6136 F 21 SAN ANTON 1 1 0

    6140 F 0 ZEEHANDLR 1 1 0

    6144 F 13 SD-WAP 1 1 0

    6148 M 0 GRAND PRA 1 1 0

    6152 M 0 AMSTERDAM 0.5 0.5 ???

    6156 F 0 ZEEHANDLR 1 1 0

    6160 M 0 GRAND PRA 1 1 0

    6164 M 7 SAN ANTON 1 1 0

    6168 M 0 ANIMALES 1 1 0

    6172 F 0 MARWELL 0.5 0.5 ???

    6176 F 1 HAI BAR 0.4816 0 ???

    6180 M 0 MARWELL 0 0 0

    6184 F 19 NZP-CRC 1 1 0

    6188 F 5 PRAHA 1 1 0.125

    6192 F 18 NZP-CRC 1 1 0

    6200 M 7 FRESNO 1 1 0.25

    6204 M 5 HOLIDAY 0 0 0

    6208 M 7 TORONTO 1 1 0.125

    6212 M 12 BRACKETT 1 1 0

    6216 F 15 DETROIT 0 0 0

    6220 F 22 TORONTO 1 1 0.125

    6224 F 2 HANNOVER 0 0 0

  • Studbook # Sex Age (y) Location % known % certain F

    36

    6228 F 21 SINGAPORE 0 0 0

    6232 M

    UNKNOWN 0 0 0

    6236 F 17 SD-WAP 1 1 0

    6240 F 16 FRESNO 1 1 0

    6244 M 5 TOKYOTAMA 1 1 0

    6248 M 0 MARWELL 0.5 0.5 ???

    6252 M 4 TOKYOTAMA 1 1 0.25

    6256 F 7 PUEBLA 1 1 0.25

    6260 F 18 MARWELL 0.9816 0.5 0.0326

    6264 F 14 HOLIDAY 1 0.5 0.125

    6268 F 0 UNKNOWN 1 1 0.125

    6272 M 0 BUSCH TAM 0 0 0

    6276 M 0 PRAHA 1 1 0.3125

    6280 F 21 SAN ANTON 1 1 0

    6284 F 1 PRAHA 1 1 0.125

    6288 F

    RABAT 1 1 0.125

    6292 M

    SOEST 1 1 0.125

    6296 F 6 HAI BAR 1 1 0

    6300 M 2 ANIMALES 1 1 0

    6304 F 17 SAN ANTON 1 1 0

    6308 F 6 HAI BAR 1 1 0

    6312 M 0 FERNDALE 1 1 0.25

    6316 M 9 MARWELL 0.9816 0.5 0.0326

    6320 F 0 MONROE 1 1 0.125

    6324 M 1 ANIMALES 1 1 0

    6328 F 0 MEMPHIS 1 1 0

    6332 F 4 PENROSE 1 1 0

    6336 F 13 SD-WAP 1 1 0

    6340 M 0 ANIMALES 1 1 0

    6344 M 0 PRAHA 1 1 0.125

    6348 F 13 SD-WAP 1 1 0.25

    6352 M 5 DALTON 1 1 0

    6356 M 3 FERNDALE 1 1 0

    6360 M 2 CZECH REP 0.9816 0.5 0.0326

    6364 F 3 LONDON RP 0.9816 0.5 0.0326

    6368 M 29 MORELIA 1 1 0.25

    6372 F 18 BULVERDE 1 0.5 0.125

    6376 F 0 MEMPHIS 1 1 0.125

    6380 M 5 UNKNOWN 1 1 0

    6384 M 0 CATSKILL 0 0 0

    6388 F 23 SILVER SP 0 0 0

    6392 F 5 BATONROUG 0 0 0

    6396 M 8 REDWOOD 0 0 0

    6400 F 8 REDWOOD 0 0 0

    6404 M 3 TORONTO 0 0 0

    6408 F 0 CATSKILL 0 0 0

    6412 F 0 CATSKILL 0 0 0

    6416 F 12 UNKNOWN 1 0 0.0625

    6420 F 12 UNKNOWN 1 0 0.0625

    6424 M 13 NZP-CRC 0 0 0

    6428 F 16 LURAY 0 0 0

    6432 F 6 DOSWELL 0 0 0

  • Studbook # Sex Age (y) Location % known % certain F

    37

    6436 M

    HANNOVER 0 0 0

    6440 F

    LONDRINA 0 0 0

    6444 F 4 HAI BAR 0 0 ???

    6448 F 0 HAI BAR 0.5 0.5 ???

    6452 M 1 HAVANA 1 1 0.25

    6456 F 1 HAVANA 1 1 0

    6460 M

    UNKNOWN 0 0 ???

    6464 F 11 BEIJING 1 1 0.25

    6468 F 12 BUSCH TAM 1 0.5 0.125

    6472 M 5 WHIPSNADE 0.4816 0 ???

    6476 M 6 WHIPSNADE 0.9816 0.5 0.0326

    6480 F 14 WHIPSNADE 0.9591 0 0.0359

    6484 F 14 PRAHA 1 1 0.125

    6488 F 3 KRECHTING 1 1 0.3125