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Re-introduction Practitioners Directory - 1998 RE-INTRODUCTION PRACTITIONERS DIRECTORY 1998 Compiled and Edited by Pritpal S. Soorae and Philip J. Seddon Re-introduction Practitioners Directory - 1998 © National Commission for Wildlife Conservation and Development, 1998 Printing and Publication details Legal Deposit no. 2218/9 ISBN: 9960-614-08-5 Re-introduction Practitioners Directory - 1998 Copies of this directory are available from: The Secretary General National Commission for Wildlife Conservation and Development Post Box 61681, Riyadh 11575 Kingdom of Saudi Arabia Phone: +966-1-441-8700 Fax: +966-1-441-0797 Bibliographic Citation: Soorae, P. S. and Seddon, P. J. (Eds). 1998. Re-introduction Practitioners Directory. Published jointly by the IUCN Species Survival Commission’s Re-introduction Specialist Group, Nairobi, Kenya, and the National Commission for Wildlife Conservation and Development, Riyadh, Saudi Arabia. 97pp. Cover Photo: Arabian Oryx Oryx leucoryx (NWRC Photo Library) Re-introduction Practitioners Directory - 1998 CONTENTS FOREWORD Professor Abdulaziz Abuzinadai PREFACE INTRODUCTION Dr Mark Stanley Price USING THE DIRECTORY ACKNOWLEDGEMENTS PART A. ANIMALS I MOLLUSCS 1. GASTROPODS 1.1 Cittarium pica Top Shell 1.2 Placostylus ambagiosus Flax Snail 1.3 Placostylus ambagiosus Land Snail 1.4 Partula suturalis 1.5 Partula taeniata 1.6 Partula tahieana 1.7 Partula tohiveana 2. BIVALVES 2.1 Freshwater Mussels 2.2 Tridacna gigas Giant Clam II ARTHROPODS 3. ORTHOPTERA 3.1 Deinacrida sp. Weta 3.2 Deinacrida rugosa/parva Cook’s Strait Giant Weta Re-introduction Practitioners Directory - 1998 3.3 Gryllus campestris Field Cricket 4. LEPIDOPTERA 4.1 Carterocephalus palaemon Chequered Skipper 4.2 Lycaena dispar batavus Large Copper 4.3 Lycaena helle 4.4 Lycaeides melissa 4.5 Papilio aristodemus ponoceanus Schaus Swallowtail 5. -
Care Sheet: Robust and Mcgregor's Skinks
Care Sheet: Robust and McGregor’s skinks Robust skink (Oligosoma alani) McGregor’s skink (Oligosoma macgregori) Adult Size: up to 150mm SVL. Adult Size: up to 114mm SVL. Threat status: ‘At Risk – Recovering’. Threat status: ‘At Risk – Recovering’. Lifespan: over 32 years. (likely over 40). Lifespan: over 35 years. Habitat: coastal forest, flaxland, deep rock Habitat: coastal forest, flaxland, boulder beaches, piles, iceplant herbfield, seabird burrows, deep deep rock piles, iceplant herbfield, seabird burrows, leaf litter and under rocks / logs. deep leaf litter and under rocks / logs. Permit Level: Conservation species. Permit Level: Insurance population species. Enclosure: Minimum recommended enclosure size = 150x70x70cm (LxWxH). Ideal Group Size: 1:1 (M:F). Compatible Species: Duvaucel’s geckos (but authorisations usually prohibit housing with other species). Recommended Cage Furnishing: The enclosure should be decorated with live plants (though these are not entirely necessary), logs, low branches for climbing, and a thick layer of leaf litter for these skinks to forage and take refuge in. Robust and McGregor’s skinks are particularly susceptible to evaporative water loss through their skin, so it is crucial that they be provided adequate damp refuge sites in the form of buried containers filled with damp leaf litter and/or damp sphagnum moss. The provision of dry refuges is also equally important as despite these lizards’ requirement for damp habitats, they will usually take refuge in cool dry refuges. Issues with skin infections can be experienced if these species are kept in conditions that are too damp where they aren’t provided adequate dry refuge sites. Refuge sites that have proved popular in captivity include rock piles, sections of bamboo or polythene pipe (with one end blocked up) buried in leaf litter, rock piles, bark stacks, hollow ponga logs, and stacks of Onduline semi-buried in leaf litter. -
Recovery Plan for Whitaker's Skink and Robust Skink
RECOVERY PLAN FOR WHITAKER'S SKINK AND ROBUST SKINK Prepared by David Towns (Science and Research Division) for Threatened Species Unit, Wellington Department of Conservation P.O. Box 10-420 Wellington NEW ZEALAND May 1992 ISSN 1170-3806 ISBN 0-478-01382-5 Threatened Species Recovery Plan Series No. 3 FOREWORD This recovery plan is one of a series of Threatened Species Unit publications produced by the Department of Conservation. Recovery plans are statements of the department's intentions for the conservation of plants and animals for a defined period. In focusing on goals and objectives for research and management, and the tasks by which these will be achieved, recovery plans serve to guide the department in its allocation of resources. Following the preparation of a technical report which was refined by scientists and managers within the department a draft of this plan was forwarded to the N. Z. Conservation Authority and relevant Conservation Boards and other interest groups for comment. After further refinement this plan was formally approved by the Director- General of Conservation on 1 April 1992. The department acknowledges the need to take into account the views of the tangata whenua and the application of their values in the conservation of natural resources. As the expression of these values may vary between iwi, it is not possible to incorporate these variations within a general theme in all recovery plans. This recovery plan will be refined and implemented in such a way as to ensure that consultation with tangata whenua of the areas in which Whitaker's and robust skinks are present has been carried out. -
Recovery Plan for Whitaker's Skink and Robust Skink
18 Increase the number of Whitaker's and robust skinks in captivity so that self-sustaining populations can be established for later release. 6. Protect populations on land outside Crown control. Establish management partnerships on locations in private ownership to ensure that their natural values as key sites for threatened lizards are not compromised. 7. Manage the mainland population of Whitaker's skink at Pukerua Bay. Establish a formally gazetted reserve at Pukerua Bay and institute management that will enhance the Whitaker's skink population. 8. Promote public interest and involvement in the recovery of Whitaker's skink and robust skink and in community restoration. Keep the public informed of progress with habitat restoration, and lizard reintroductions, involve interested groups as appropriate and provide for long term public participation. CRITICAL PATH 19 8. RECOVERY STRATEGY: WORK PLAN To meet each objective and the fulfil the recovery goals the following actions are required: OBJECTIVE 1. ERADICATE RODENTS FROM LARGE ISLANDS Explanation Restoration of island biotic communities relies on efficient techniques for eradication of rodents. Successful cost-effective techniques have been developed for small islands, but these tend to be labour intensive (McFadden and Towns 1991). Mechanical techniques for air drops of rodenticide will need to be applied to islands of 100 ha or more if the options defined in this plan are to be met. Plan Aerial drops by helicopter using TALON 20P provided gratis by a chemical company began in September 1991 on Stanley Island (100 ha). If successful it may be extended to Red Mercury Island in 1992. Outcomes The eradication campaign against kiore (as well as rabbits) on Stanley and Red Mercury Islands will: Rehabilitate two populations of tuatara Release invertebrates from predation by kiore Provide two very large islands with considerable suitable habitat for Whitaker's and robust skinks. -
Mana Island Ecological Restoration Plan
9. Reptiles Designing a future reptile community on Mana Island required information on: what indigenous species are currently present what species are likely to have been present historically what nationally or regionally threatened species require habitats free of introduced mammals to ensure their continued survival, and whether there are other more appropriate sites for their introduction potential conflicts between proposed introductions and resident species and/ or other proposed introductions (including invertebrates and other reptiles), e.g., predation, competition, disease risk, hybridization. Mana island already has nationally important populations of two threatened lizard species (McGregor's skink and goldstripe gecko) and it is essential that future introductions and habitat management do not jeopardise their survival. The list of reptiles recorded from the entire Cook Strait Ecological District is not an appropriate model for guiding restoration of Mana Island's reptile fauna, as many lizard taxa do not occur on both sides of Cook Strait. Of 17 lizard species recorded from Cook Strait Ecological District, only eight (47%) occur on both sides of Cook Strait (Table 9.1). Most notably, Cook Strait is the southern limit of the skink genus Cyclodina, five species of which occur (or occurred) in the Wellington region. TABLE 9.1 REPTILE SPECIES RECORDED FROM COOK STRAIT ECOLOGICAL DISTRICT, WITH A SUMMARY OF PAST AND PRESENT DISTRIBUTION ON BOTH SIDES OF COOK STRAIT. NOTE THAT PACIFIC GECKOS OCCUR NEARBY IN THE WELLINGTON ECOLOGICAL DISTRICT, AND WERE PROBABLY PART OF THE ORIGINAL COOK STRAIT REPTILE FAUNA. OGLE (1989a) RECOMMENDED THAT THE TWO SIDES OF COOK STRAIT BE INCLUDED IN DIFFERENT ECOLOGICAL REGIONS OR DISTRICTS BASED ON DIFFERENCES IN FAUNA EITHER SIDE OF THE STRAIT. -
The Relationship of Herpetofaunal
Georgia Southern University Digital Commons@Georgia Southern Electronic Theses and Dissertations Graduate Studies, Jack N. Averitt College of Spring 2009 The Relationship of Herpetofaunal Community Composition to an Elephant (Loxodonta Africana) Modified Savanna oodlandW of Northern Tanzania, and Bioassays with African Elephants Nabil A. Nasseri Follow this and additional works at: https://digitalcommons.georgiasouthern.edu/etd Recommended Citation Nasseri, Nabil A., "The Relationship of Herpetofaunal Community Composition to an Elephant (Loxodonta Africana) Modified Savanna oodlandW of Northern Tanzania, and Bioassays with African Elephants" (2009). Electronic Theses and Dissertations. 763. https://digitalcommons.georgiasouthern.edu/etd/763 This thesis (open access) is brought to you for free and open access by the Graduate Studies, Jack N. Averitt College of at Digital Commons@Georgia Southern. It has been accepted for inclusion in Electronic Theses and Dissertations by an authorized administrator of Digital Commons@Georgia Southern. For more information, please contact [email protected]. THE RELATIONSHIP OF HERPETOFAUNAL COMMUNITY COMPOSITION TO AN ELEPHANT ( LOXODONTA AFRICANA ) MODIFIED SAVANNA WOODLAND OF NORTHERN TANZANIA, AND BIOASSAYS WITH AFRICAN ELEPHANTS by NABIL A. NASSERI (Under the Direction of Bruce A. Schulte) ABSTRACT Herpetofauna diversity and richness were compared in areas that varied in the degree of elephant impact on the woody vegetation ( Acacia spp.). The study was conducted at Ndarakwai Ranch in northeastern Tanzania. Elephants moving between three National Parks in Kenya and Tanzania visit this property. From August 2007 to March 2008, we erected drift fences and pitfall traps to sample herpetofaunal community and examined species richness and diversity within the damaged areas and in an exclusion plot. -
A Biological Survey of the Murray Mallee South Australia
A BIOLOGICAL SURVEY OF THE MURRAY MALLEE SOUTH AUSTRALIA Editors J. N. Foulkes J. S. Gillen Biological Survey and Research Section Heritage and Biodiversity Division Department for Environment and Heritage, South Australia 2000 The Biological Survey of the Murray Mallee, South Australia was carried out with the assistance of funds made available by the Commonwealth of Australia under the National Estate Grants Programs and the State Government of South Australia. The views and opinions expressed in this report are those of the authors and do not necessarily represent the views or policies of the Australian Heritage Commission or the State Government of South Australia. This report may be cited as: Foulkes, J. N. and Gillen, J. S. (Eds.) (2000). A Biological Survey of the Murray Mallee, South Australia (Biological Survey and Research, Department for Environment and Heritage and Geographic Analysis and Research Unit, Department for Transport, Urban Planning and the Arts). Copies of the report may be accessed in the library: Environment Australia Department for Human Services, Housing, GPO Box 636 or Environment and Planning Library CANBERRA ACT 2601 1st Floor, Roma Mitchell House 136 North Terrace, ADELAIDE SA 5000 EDITORS J. N. Foulkes and J. S. Gillen Biological Survey and Research Section, Heritage and Biodiversity Branch, Department for Environment and Heritage, GPO Box 1047 ADELAIDE SA 5001 AUTHORS D. M. Armstrong, J. N. Foulkes, Biological Survey and Research Section, Heritage and Biodiversity Branch, Department for Environment and Heritage, GPO Box 1047 ADELAIDE SA 5001. S. Carruthers, F. Smith, S. Kinnear, Geographic Analysis and Research Unit, Planning SA, Department for Transport, Urban Planning and the Arts, GPO Box 1815, ADELAIDE SA 5001. -
Best Practice Guide to Keeping New Zealand Lizards in Captivity
GUIDE TO KEEPING NEW ZEALAND LIZARDS IN CAPTIVITY Richard Gibson This Best Practice Guide has been written to help you understand how to best care for the native New Zealand lizards you hold in captivity and how you can meet your obligations under your Wildlife Act Authorisation. The Guide outlines broad principles some practical steps to help you meet the conditions of your Authorisation. The Guide provides general advice; it is not possible to deal with every situation that may arise. When using this Guide, discretion and judgement will be needed and it may be necessary to seek expert assistance. The Guide is regarded as a ‘living document’ which will be regularly reviewed and updated as necessary. Readers are encouraged to send in feedback so that the guidelines can be further improved through an ongoing process of communication and co-operation. To contribute, please contact [email protected]. All material in this publication, with the exception of photographs, is licensed under the Creative Commons Attribution 4.0 International Licence etc. If you wish to cite this guide please use the following format: Guide to keeping New Zealand lizards in captivity. Department of Conservation, Wellington - 2 - CONTENTS 1. Understanding the needs of an ectotherm 2. Housing native lizards – the vivarium 3. Handling and restraint 4. Nutrition and feeding 5. Breeding New Zealand lizards 6. Identification and record keeping 7. Transporting lizards 8. Lizard health and hygiene Glossary of terms Appendix 1: Products, materials and suppliers Appendix 2: Properties of different vivarium materials Appendix 3: Auckland Zoo native skink/gecko diet guideline Appendix 4: Quick guide for commonly kept species Further reading - 3 - 1. -
Determining Priority Areas for an Endangered Cold-Adapted Snake on Warming Mountaintops
Determining priority areas for an Endangered cold-adapted snake on warming mountaintops E DVÁRD M IZSEI,MÁRTON S ZABOLCS,LORÁND S ZABÓ,ZOLTÁN B OROS K UJTIM M ERSINI,STEPHANOS A. ROUSSOS,MARIA D IMAKI Y ANNIS I OANNIDIS,ZSOLT V ÉGVÁRI and S ZABOLCS L ENGYEL Abstract Spatial prioritization in systematic conservation areas for the conservation of single species. Our study planning has traditionally been developed for several to demonstrates that spatial prioritization for single umbrella, many species and/or habitats, and single-species applica- flagship or keystone species is a promising approach for the tions are rare. We developed a novel spatial prioritization conservation of species for which few data are available. model based on accurate estimates of remotely-sensed data Keywords Climate change, habitat suitability, land use, and maps of threats potentially affecting long-term species protected area, range shift, reptile, spatial conservation persistence. We used this approach to identify priority areas planning, Vipera graeca for the conservation of the Endangered Greek meadow viper Vipera graeca, a cold-adapted species inhabiting mountain- Supplementary material for this article is available at tops in the Pindos Mountains of Greece and Albania. We doi.org/./S transformed the mapped threats into nine variables to esti- mate conservation value: habitat suitability (climate suitabil- ity, habitat size, occupancy, vegetation suitability), climate change (future persistence, potential for altitudinal range Introduction shift) and land-use impact (habitat alteration, degradation, iological diversity has experienced significant losses as disturbance). We applied the Zonation systematic conserva- a result of a number of factors that directly or indi- tion planning tool with these conservation value variables as B rectly affect species. -
Determining Priority Areas for an Endangered Cold-Adapted Snake on Warming Mountaintops
Determining priority areas for an Endangered cold-adapted snake on warming mountaintops E DVÁRD M IZSEI,MÁRTON S ZABOLCS,LORÁND S ZABÓ,ZOLTÁN B OROS K UJTIM M ERSINI,STEPHANOS A. ROUSSOS,MARIA D IMAKI Y ANNIS I OANNIDIS,ZSOLT V ÉGVÁRI and S ZABOLCS L ENGYEL Abstract Spatial prioritization in systematic conservation areas for the conservation of single species. Our study planning has traditionally been developed for several to demonstrates that spatial prioritization for single umbrella, many species and/or habitats, and single-species applica- flagship or keystone species is a promising approach for the tions are rare. We developed a novel spatial prioritization conservation of species for which few data are available. model based on accurate estimates of remotely-sensed data Keywords Climate change, habitat suitability, land use, and maps of threats potentially affecting long-term species protected area, range shift, reptile, spatial conservation persistence. We used this approach to identify priority areas planning, Vipera graeca for the conservation of the Endangered Greek meadow viper Vipera graeca, a cold-adapted species inhabiting mountain- Supplementary material for this article is available at tops in the Pindos Mountains of Greece and Albania. We doi.org/./S transformed the mapped threats into nine variables to esti- mate conservation value: habitat suitability (climate suitabil- ity, habitat size, occupancy, vegetation suitability), climate change (future persistence, potential for altitudinal range Introduction shift) and land-use impact (habitat alteration, degradation, iological diversity has experienced significant losses as disturbance). We applied the Zonation systematic conserva- a result of a number of factors that directly or indi- tion planning tool with these conservation value variables as B rectly affect species. -
Threatened Flora and Fauna Species and Non-Threatened Vertebrate Fauna in the Goulburn Broken Catchment: Status, Trends and Management
Threatened flora and fauna species and non-threatened vertebrate fauna in the Goulburn Broken Catchment: status, trends and management Background paper to the Goulburn Broken Catchment Regional Catchment Strategy review process. Paul Ryan Ecolines Environmental Services Canberra June 2002 Disclaimer This report was prepared for the general purpose of assisting with the Goulburn Broken Regional Catchment Strategy review and update. An exhaustive investigation was not appropriate for this purpose. The report is based on the best readily available information. The views expressed in the report are those of the author and do not necessarily represent the views of the GBCMA. Neither the author nor the Goulburn Broken Catchment Management Authority assumes any liability resulting from the use or reliance of its contents. 2 Table of Contents 1. Summary of Recommendations..................................................................................5 1.1. Strategic Planning...............................................................................................5 1.2. Communication...................................................................................................7 1.3. Implementation...................................................................................................7 2. Introduction.................................................................................................................9 2.1. Aim and scope of this background paper............................................................9 2.2. Decision -
Reptiles & Amphibians
AWF FOUR CORNERS TBNRM PROJECT : REVIEWS OF EXISTING BIODIVERSITY INFORMATION i Published for The African Wildlife Foundation's FOUR CORNERS TBNRM PROJECT by THE ZAMBEZI SOCIETY and THE BIODIVERSITY FOUNDATION FOR AFRICA 2004 PARTNERS IN BIODIVERSITY The Zambezi Society The Biodiversity Foundation for Africa P O Box HG774 P O Box FM730 Highlands Famona Harare Bulawayo Zimbabwe Zimbabwe Tel: +263 4 747002-5 E-mail: [email protected] E-mail: [email protected] Website: www.biodiversityfoundation.org Website : www.zamsoc.org The Zambezi Society and The Biodiversity Foundation for Africa are working as partners within the African Wildlife Foundation's Four Corners TBNRM project. The Biodiversity Foundation for Africa is responsible for acquiring technical information on the biodiversity of the project area. The Zambezi Society will be interpreting this information into user-friendly formats for stakeholders in the Four Corners area, and then disseminating it to these stakeholders. THE BIODIVERSITY FOUNDATION FOR AFRICA (BFA is a non-profit making Trust, formed in Bulawayo in 1992 by a group of concerned scientists and environmentalists. Individual BFA members have expertise in biological groups including plants, vegetation, mammals, birds, reptiles, fish, insects, aquatic invertebrates and ecosystems. The major objective of the BFA is to undertake biological research into the biodiversity of sub-Saharan Africa, and to make the resulting information more accessible. Towards this end it provides technical, ecological and biosystematic expertise. THE ZAMBEZI SOCIETY was established in 1982. Its goals include the conservation of biological diversity and wilderness in the Zambezi Basin through the application of sustainable, scientifically sound natural resource management strategies.