NATIONAL REPORT ON THE CONVENTION ON MIGRATORY SPECIES OF WILD ANIMALS Report prepared by: Dr. B.Lkhagvasuren CMS Scientific Councilor for Mongolia WWF Mongolia Programme Office Institute of Biology, MAS P.B.O-20а/115, Ulaanbaatar 210620А. Email: lkhagvasuren@wwf.mn Ulaanbaatar 2012 1 National Report on The Convention on Migratory Species Requested by: Ministry of Nature, Environment, and Tourism Funding Agencies: United Nations Development Programme WWF Mongolia Programme Office Partners: Ministry of Nature, Environment, and Tourism CMS National Council Institute of Biology, Mongolian Academy of Sciences Mongolian Ornithological Society Ulaanbaatar 2012 2 A Table of Contents FOREWORD 4-5 BACKGROUND INFORMATION ON MONGOLIA AND ITS NATURAL STATE 6-9 BRIEF INTRODUCTIONS ON ENVIRONMENTAL CONVENTIONS, INTERNATIONAL TREATIES AND AGREEMENTS WHICH MONGOLIA HAS SIGNED 9-11 CONVENTION ON THE CONSERVATION OF MIGRATORY SPECIES OF WILD ANIMALS/BONN CONVENTION 11-14 The Convention functions The Convention’s main bodies The Convention’s Contracting Parties The Convention’s Standing Committee The Convention’s Scientific Council The Convention Secretariat MONGOLIA AND THE BONN CONVENTION 1526 Brief introductions on conservation efforts undertaken for migratory wild species before Mongolia adopted the Convention Brief introductions on conservation efforts undertaken for migratory wild species after Mongolia adopted the Convention BRIEF DESCRIPTIONS OF THE SPECIES LISTED IN THE APPENDIX TO THE BONN CONVENTION 2737 DECISIONS OF MEETINGS OF THE COP TO THE CONVENTION AND THEIR FOLLOW UP ACTIONS IN MONGOLIA 38-43 SUCCESS, CONSTRAINTS, & LESSONS LEARNT DURING THE FOLLOW UP ACTIONS OF THE DECISIONS 44-46 FUTURE ACTIONS: COMMENTS & RECOMMENDATIONS 47-49 ACKNOWLEDGEMENTS 49 REFERENCES 50-54 3 ANNEXES 54-73 4 FOREWORD The living styles and patterns of the Mongolians are well harmonized with the harsh continental climate and natural conditions with specific traditions and customs providing the country’s people with opportunities to keep up appropriate communications with the nature and environment and share benefits from its abundant but somehow vulnerable natural resources e.g. wildlife, forests, water, and natural springs. We did not bypass the humans’ development process. On the contrary, the development process has intensively taken place in the country during the last half of the century and considerable scientific and technological progress has been introduced in the country. During this progress taken in the country, traditional living styles and customs are likely to be forgotten and seem only as occasional applications in practice. As a result of these changes, some parts of the biodiversity that seemed to be non-exhaustive are being threatened with loss and extinction at the present time. In addition to this human development process, some other natural factors e.g. climate change and climate warming, are giving additional pressure to nature and the environment, aggravating the situation. Recognizing these disadvantages, a number of countries in the world are paying attention to and taking appropriate measures for environmental conservation, sustainable use, and the enhancement of natural resources. However, conservation efforts by an individual country are not totally sufficient enough for tackling the current environmental concerns. Thus, the countries around the world are endeavoring to cooperate in environmental conservation. Otherwise, natural conditions are becoming impaired and extinction is likely to be faced occasionally. The collaborative forms e.g. the international Conventions, treaties, agreements, and coalitions, have become the most efficient and prompt tools for tackling the pressing global issues and upgrading cooperation among the countries around the world. Thus, international communities have initiated a number of environmental Conventions, where many countries have joined. Having signed these Conventions, Mongolia has actively taken part in their activities and have been fulfilling its commitments. Many of the international Conventions are willing to carry out conservation efforts with conservation of specific biological species or habitats. Due to a number of reasons e.g. climate change, lack of food and prey, and their breeding and calving seasons (those are regarded as important, but vulnerable for each species), many wild species spend certain periods of the year in areas different from their usual habitat. When some wild species move and migrate into more favorable conditioned areas, some others move into different areas during their breeding and rutting seasons. During their migrations and movements, wild animals face a number of challenges and obstacles with quite a considerable amount of loss to their populations. Migrations and movements of terrestrial and aquatic vertebrate species into far distances are the ecological process that has been taking place for several hundreds of years, not for millions of years. However, our knowledge and understanding on wildlife migrations and movements is inadequate, and many risks are faced to the conservation of numerous migratory wildlife species due to the high impact of human activity. For efficient conservation of migratory wildlife species, the trans-boundary movements and migrations of wildlife species should be sufficiently supported by scientific and policy considerations. , The countries of the world recognized the importance of these efforts and adopted the Convention of Migratory Species of Wild Animals in 1979,which came into force on November 1, 1983. as the convention has become known as the Bonn Convention after the place where it was first adopted. The Parties to the Convention have the responsibilities to protect the wild species including migratory birds, terrestrial and aquatic (seas, oceans, 5 rivers, lakes, and wetlands) wild species inhabiting and migrating within and passing through their territories within their natural habitats and distribution areas. Currently, 116 countries in the world have signed the Convention. Adopting the Convention on Migratory Species of Wild Animals during the Parliament session of June 24, 1999, Mongolia first participated in the 6th meeting of the Conference of Parties (COP) to the Convention. Since it joined the Bonn Convention, Mongolia has been active in Convention activities and events. These include some trans-boundary migratory species in the Convention Appendix, the development of respective document drafts through its Scientific Council to make contributions and inputs in Decisions of COP, and the implementation of the actions of the Memorandums of Understanding which Mongolia has signed. For instance, Mongolia successfully organized the second meeting of Parties to the Memorandum of Understanding on Saiga Conservation in Ulaanbaatar. It was an important step to unite conservation efforts of international communities for the species conservation. Although Mongolia has been active in the fulfillment of its commitments and implementation of the Convention COP meetings, decisions in practice (as mentioned above), public awareness and promotional activities are still inadequate. The Ministry of Nature, Environment, and Tourism recognized these needs by initiating the comprehensive national reports on the actions implemented within the framework of the Bonn and Ramsar Conventions and the task to prepare the national reports has been completed with support and funding from the UNDP Country Office and WWF Mongolia Programme office. We are sure that this report will be an important baseline document for future research and conservation of migratory wild species in Mongolia. This report may be missing some other important piece of information, data, facts, and references on migratory wild species. Therefore, we are cordially inviting all of you, who want to share their comments and feedback, to contact to D. Batbold, the Chairman of National Council of Bonn Convention, and B. Lkhagvasuren, Dr.Sc. Advisor to the Convention Scientific Council. D. Batbold, Director of International Cooperation Department, MNET & CMS Focal Point for Mongolia: (dbatbold@mne.gov.mn) B. Lkhagvasuren, Dr., CMS Scientific Councilor for Mongolia & WWF Mongolia Programme Office, Programme Coordinator, Senior scientist, Institute of Biology, Mongolian Academy of Sciences: (lkhagvasuren@wwf.mn) 6 Background information on Mongolia and its natural state Mongolia is a landlocked country located in East and Central Asia, situated on the Mongolian steppe. It borders the Russian Federation in the north and the People’s Republic of China to the south. It is close to Kazakhstan in the west (the distance between the countries’ border points is 38 km). About 45 per cent of Mongolia’s total population resides in Ulaanbaatar, the capital and largest city in the country. In terms of its political governance, Mongolia is a Republic with a unicameral Parliament. The head of state is the President of Mongolia, the head of Government is the Prime Minister of Mongolia, and the legislative body or the Supreme State organization is the State Great Khural. The population is 2.75 million, consisting of Mongol (95%), Kazakh (3.9%), Durvud, and other ethnic groups. Mongolia is a landlocked country and the predominant religion is Buddhism. Mongolia ranks 17th in its territory size,. Total area is 1,564,116 sq. km and the average elevation is 1,580 m above sea level. it is a sparsely populated country. The majority of the country’s territory consists of steppe. The Altai, Khangai, and Khentii mountain ranges stretch through the north and west, while the Gobi is dominant in the south. The main agricultural sector is pastoral animal husbandry. Wheat and vegetables are mainly cultivated in rivers basins. Mongolia is rich in mineral resources such as coal, iron ore, and zinc. Natural zones: From the north to the south, there are four zones: forest steppe, steppe, Gobi, and desert. In high mountainous areas, particularly in forest steppe region, there are boreal coniferous forest and alpine zones. As per the existing natural zones, Mongolia is divided into four topographic areas: Khangai, Khentii and Altai mountainous areas, Eastern steppe, and Gobi. Natural and climatic conditions: Situated in the northern Asian mountainous area, Mongolia lies in the middle latitude of the Northern Hemisphere of the globe. According to the climatic classifications, it lies in the temperate zone. Mongolia has an extreme continental climate. In terms of its landscape, it supports uneven landforms e.g. high mountains of different shapes and locations, flat plains, vast steppe, big lakes and rivers, and landforms with and without vegetations co-occurring. This diversity shows the country supports specific natural and climatic states. The maximum air temperature recorded by a local meteorological station was +44.80 С in Ekhiin River valley in the territory of Shinejinst Soum of Bayankhongor Aimag, while the minimum air temperature was -56,60 С in Zuun Gobi Soum of Uvs Aimag. The difference between the absolute high and low temperatures was 100.40 С in the country (Institute of Hydrology and Meteorology, 2009). Soil Mongolia supports various types of soils e.g. kastanozems, brown, dark brown, light brown, chernozems, meadow brown, Gobi brown, desert brown gray, meadow, marshy, and saline. Among these different types of soils, nutritive kastanozems are about 50 per cent. Arable land, suitable for farming or cultivation, is 0.76% of the country’s total territory. Irrigated land is 840 km². 7 Water Mongolia has 6,646 rivers and streams running a distance of 67,000 km. Out of these rivers and streams, 6,095 rivers and streams are running, while 551 rivers and streams have been lost or dried up. There are over 3,600 lakes occupying an area of 500 m³, about 10,500 natural springs, about 225 glaciers occupying 540 m² area, and over 260 mineral water bodies in the country. There are 139 ground water deposits. Ulaanbaatar city is one of two Capital Cities in the world supported by mineral water bodies inside the cities. The largest glacier in Mongolia is “Potanin” located on Altai Tavan Bogd Mountain and is about 20 km long. Rivers in Mongolia are basically classified as rivers of the northern Arctic Ocean, rivers of Pacific Ocean, and rivers of the closed Central Asian drainage basin. The longest river in Mongolia is Orkhon River (length is 1,124 km and its water catchment area is 133,000 km²). Another major or long river is Kherlen River. If the part running through the People’s Republic of China is added to the part running through the territory of Mongolia, the Kherlen River (1,200 km) will be the longest river in Mongolia. Most of the river (about 1090 km) runs through the Mongolian territory. The river with the maximum amount of water is Selenge River. Its mean annual run-off is 300 m3/sec. The largest lake in the country is Uvs Lake (3350 km²), while the deepest lake is Khovsgul Lake (262.4 m). As per the references, the depth of Khovsgul Lake differs from 268 meters to 261 meters. Flora and fauna: There are 348 woody and shrubbery species and 2,095 herbaceous species recorded in Mongolia. Among the woody plants recorded, there are 17 tree species, 40 small tree or big shrubbery species, 146 shrubbery species, 48 semi-shrubbery species, 91 semi-shrubs, and 6 liana species . There are 1,765 perennial species, 330 years species and two years old vascular plants recorded in the country. Among these plants, there are also 21 species of flat moss, coniferous moss of 38 families, 1,236 lichen species of 53 families, a sub-algae, and over 900 species of fungi recorded in the country. About 600 species belonging to different families and genera are recorded as 8 pastureland and fodder plants. Out of these plants, over 100 species are regarded as edible and nutritious for livestock. These species provide for the majority of hay making and pastureland plant yields in the country. As Mongolia supports different natural, climatic, and geographic conditions, it provides a home to diverse representatives of fauna and flora species on the Earth. There are 138 mammal species, over 490 bird species, 75 fish species, six species of amphibians, and 22 species of reptiles recorded in Mongolia. From the invertebrates, there are 13,000 species of insects, other mollusks, and 516 protozoans recorded (Biodiversity Action Plan of Mongolia, 2009). Physical-geographical features: Mongolia is located in the heart of Asia, between two powerful States: the People’s Republic of China and the Russian Federation. It supports the Siberian boreal coniferous forests in the northern part, and the edges of Central Asia in the southern part of the country. Thus, the Mongolian territory provides for a transitional strip zone of these regions. With a total territory of 1,564,100 km2stretching from the west to the east in an oval shape, it is situated in the middle latitude of the Northern Hemisphere of the globe. It belongs to the temperate zone as per the climate classification. The country’s territory covers 1 percent of land on the Earth. The total border length is 8158 km including 3,485 km with the Russian Federation and 4,678 km with China. Mongolia’s territory size ranks 17th in the world and 7th in Asia. The mean elevation in Mongolia is 1,580 m, the maximum height is 4,374 m (Khuitnii Orgil, Altai Tavan Bogd Mountain) and the lowest point is 560 m (Khukh Lake depression). The areas bordering both Russia or China are Khuitnii Orgil in Bayan-Ulgii Aimag and Tarvagan Dahiin Ovoo in Dornod Aimag. Most part of the country’s territory is elevated relatively high above the sea level, for instance, 80% of total territory lies at more than 1000 m, the average elevation is 1,580 m. These specific locations e.g. mountainous and relatively elevated areas make climate more temperate and drier, but hold true desert conditions. The splendid Khentii, Khangai, and Sayan Mountains continue in the central and northern parts of Mongolia. The highest peak of the Khangai Mountains is Enkhtaivan Mountain (3,900 m), the highest peak of the Khentii Mountains is Asralt Khairkhan Mountain (2800 m). In the eastern part of Mongolia, there is a continuation of mountains of the Great Khyangan Mountains. The steppe is abundant in the eastern and southern parts of Mongolia The largest steppe, the Eastern steppe, covers about 250,000 km2. The steppe supports the Khukh Lake depression, the lowest point in the country. In addition to the Eastern steppe, the Great Lakes depression located between Altai and Khangai Mountain ranges, and the Gobi region known as “Zag Suuj” and “Nomin’s 33 Gobi” in the southern part of the country are basically steppe regions. Rivers in the area are divided into three major basins’ (Pacific Ocean, Northern Arctic, and closed drainage) watersheds. Many of the sources of these three watersheds lie in Mongolia. In wintertime, the area’s maximum air pressure zone is recorded in Uvs Lake depression. Thus, extremely high air pressure is accumulated in winter and gradually sustained in the depression. Supported and covered by different types of natural zones and regions e.g. high mountains, alpine, boreal coniferous forests, forest steppe, steppe, Gobi, and desert, Mongolia is situated in a transition zone of the Siberian boreal coniferous forests in the world’s temperate zone to the Central Asian Gobi and desert. Thus, a temperate zone cyclone and anti-cyclone predominantly shift throughout the Mongolian territory. 9 Annual precipitation amount is 200-220 mm, but it is 400-500 mm in the Khangai region, 200-300 mm in the Eastern steppe, and 100-150 mm or less in the Gobi depending on their landforms. Brief Introductions on Environmental Conventions, International Treaties and Agreements, where which Mongolia has signed: The Convention on Wetlands of International Importance, especially as Waterfowl Habitat‘Ramsar Convention’ The first Convention on biodiversity conservation is the Convention on Wetlands of International Importance, especially as Waterfowl Habitat, that was established in Ramsar, Iran on February 2, 1971 (Introductions on the Conventions on biodiversity conservation, 2011). Its 40th anniversary was held in 2011. A detailed report on the Convention was separately developed. Convention on International Trade in Endangered Species of Wild Fauna and Flora /CITES Mongolia signed the Convention on April 4, 1996 and was listed as the 133 Contracting Party., A total of 14 species of mammals, 71 species of birds, eight species of plants, two species of fish, one species of insect, and one species of reptile are listed in the Convention Appendices 1 and 2. To coordinate the implementation of the Convention on International Trade of Endangered Species of Wild Fauna and Flora, the Managing and Coordinating and Scientific Councils have been established according to Article 9:1b of the Convention, Articles 2 & 4 of the Law on Regulation of International Trade in Endangered Species of Wild Fauna and Flora, Articles 23 & 24 of the Law on Fauna , and Article 17:1 of the Law on Natural Plants (Introduction on the Conventions on Biodiversity Conservation, 2011). 10 Convention on Biodiversity /CBD It is the first worldwide Convention that addresses the ecosystem, all biological species, genetic resources, and their sustainable use and consumption and conservation. In addition to these, it provides the global legal framework for action on biodiversity recognizing that conservation is an indispensible part of the humans’ development and in the common interest of humans. The Convention is the document linking traditional environmental conservation practices with the economic purpose addressed at sustainable use of biological resources. The Cartagena Protocol on Biosafety to the Convention on Biological Diversity aims at the biotechnological issues e.g. technological advances, technological transfers, and balancing the share of benefits for those that have rapidly developed in recent years. The Convention on Biodiversity carries out its functions in accordance with international legislations under the following three goals: 1. The conservation of biological diversity 2. The sustainable use of the components of biological diversity 3. The fair and equitable sharing of the benefits arising out of the utilization of genetic resources. Under the objectives above, it focuses on development of strategic national planning on biodiversity conservation and sustainable use. In 1992, the Prime Minister of Mongolia signed the Convention during the conference of UN Environment and Development held in Rio De Janeiro. The Parliament of Mongolia adopted the Convention on June 1, 1993. The Cartagena Protocol on Biosafety to the Convention on Biological Diversity aims at the biotechnological issues e.g. technological advances, technological transfers, and balanced share of benefits that have rapidly developed in recent years (Introduction on the Conventions on Biodiversity Conservation, 2011). Cartagena Protocol Mongolia adopted the Protocol on November 25, 2002. The Protocol has been signed by 160 countries around the world. The Cartagena Protocol on Biosafety to the Convention on Biological Diversity aims at safe handling of modern biotechnology. The main purpose of the Protocol is to ensure the biodiversity conservation and sustainable use, and safe handling, transport and use of living modified organisms (LMOs) resulting from modern biotechnology that may have adverse effects on biological diversity while paying special attentions during transporting through State borders. To support the implementation of the Biodiversity Strategic Plan for 2011-2020 adopted from the 10th meeting of Contracting Parties on the Convention on Biodiversity, 2011-2020 has been announced as the UN Decade for Biodiversity. The Convention Secretary was assigned to manage the task to celebrate the Decade on behalf of the UN meeting member countries with support from the Convention Secretariat, other related Conventions, UN Funds, programmes, and agencies. Meantime, the member countries were also called up to actively & voluntarily take part in the Decade events as providing financial and other necessary support to the events. The Decade announced overlaps with the implementation period of the Biodiversity Strategic Plan for 2011-2020 adopted on the 10th meeting of the COP held in Nagoya , Japan (Introduction on the Conventions on Biodiversity Conservation, 2011). 11 Convention on Migratory Species of Wild Animals /Bonn Convention Justification, scope, and purpose: Migratory species face a number of pressures and threats e.g. overharvesting, food deficiency, and loss of breeding sites during their migratory flyways. Identifying and recognizing these pressures and threats to the species, countries around the world adopted the Convention on Migratory Species (CMS) in 1979 and it came into force on November 1, 1983 ( Introduction on the Conventions on Biodiversity Conservation, 2011). It was initially called the Bonn Convention, after the place where it was first convened. The Contracting Parties to the Convention on Migratory Species of Wild Animals are obliged to conserve terrestrial, aquatic and avian migratory species throughout their ranges. Currently, 116 countries have signed the Convention. The following actions are undertaken within the Convention framework: 1.If a migratory species population has faced a threat to become extinct entirely or partially within its habitat or range, the country or a Party to the Convention will take special action for conservation of the species population (for the species listed in the Convention Appendix I); 2. If a migratory species needs more efficient conservation action or it needs to be protected through international communities’ conservation efforts, the countries will make an agreement or treaty for efficient conservation management of the migratory species (for the species listed in Appendix 2); 3.Joint research and monitoring will be conducted; For the conservation of the species listed in Appendix 2, the Convention manages and handles conclusion of regional agreements and treaties. Currently, seven agreements and 19 Memorandums of Understanding have been signed. Contracting Parties to the Convention meet on triennial basis, the Scientific Council meets once per 1.5 years. The Contracting Parties send their national reports to the Convention Secretariat six months in advance from the next COP date. The table below shows the countries which have organized COPs. No 1 2 3 4 5 6 7 8 9 10 Cities of the countries, where regular COPs Date of regular were held: COPs Bonn, Germany 1985 Geneva, Switzerland 1988 Geneva, Switzerland 1991 Nairobi, Kenya 1994 Geneva, Switzerland 1997 Cape Town, South Africa 1999 Bonn, Germany 2002 Nairobi, Kenya 2005 Rome, Italy 2008 Bergen, Norway 2011 12 The COP establishes and keeps the financial regulations of the Convention under review. Each COP meeting reviews the Convention implementation with focus on the following actions: • Identify and assess migratory species’ status; • Review the progress made in conservation of the migratory species particularly listed in the Convention Appendices 1 & 2; • Enable the Scientific Council and Secretariat to run their operations and provide them with guidance; • Accept and discuss about reports of Scientific Council, Secretariat, COP, and other bodies & agencies established as per the agreements; • Provide the COP with recommendations on improvements of migratory species conservation status and review the progress made under the agreements; • In the event where no agreements are made, discuss about the status of migratory species’ conservation and make recommendations on call for irregular meetings of COP in the regions where the species habitats and ranges lay; • Forward recommendations on improved Convention efficiency to the COPs; • Make decisions on necessary additional actions for adequate implementation of the Convention; Standing Committee: The Standing Committee was established by Resolution 1.1 of the Conference of the Parties. Its functions are to provide policy and administrative guidance between regular meetings of the Conference of the Parties. It consists of representatives of every global region, of the Depositary, and where applicable, of the country which plans to host the next meeting of the COP. The table below shows the Standing Committee members (elected on the 10th meeting of COP held in Bergen) and the current members: REGIONS MEMBERS ALTERNATIVE MEMBERS Africa Ghana (chair) Tunisia Uganda Congo Mali South Africa Asia India Pakistan Mongolia Syria South & Central America & Caribbean Chile Cuba Argentina (not elected yet) Europe Norway (ViceChair) Poland Ukraine France Georgia Switzerland North America vacant vacant Oceania New Zealand Australia Depositary Germany 13 (Brazzaville) Host of COP10 Norway (also representative for Europe) Host of COP11 to be confirmed Scientific Council: The establishment of a Scientific Council to provide advice on scientific matters is foreseen in Article VIII of the Convention. The Council makes recommendations to the Conference on such issues as research on migratory species, specific conservation and management measures, the inclusion of migratory species in the Appendices and designation of species for Cooperative Actions under the Convention. It also gives advice on projects' eligibility for funding under the Small Grant Programme of CMS. Each Party is entitled to appoint a qualified expert as a member of the Scientific Council. Parties may also nominate an alternate Scientific Councilor, entitled to participate in meetings of the Council when the regular Councilor cannot attend. In addition to the members appointed by the individual Parties, the Conference of the Parties can appoint to the Council other experts to cover fields of particular interest to the Convention. As of April 2008, the Council included eight Conference-appointed members to cover the following threats to: marine turtles; birds; aquatic mammals; fish; neo-tropical fauna; Asiatic fauna; African fauna. At present, there are about 88 members of the Council. Secretariat: The CMS Secretariat is the Convention's coordinating body. It arranges for and services meetings of the Conference of the Parties (COP), the Scientific Council (ScC) and the Standing Committee (StC). Its functions are enumerated in Article IX of the Convention: “The Secretariat promotes and supports the development of Agreements, supports and supervises research and conservation projects, disseminates information and co-operates with governments and partner organizations”. The CMS Secretariat is provided and administered by the United Nations Environment Programme (UNEP). Since its establishment the Secretariat has been located in Bonn, Germany. In 1998, the Secretariat, which had been previously colocated with the Federal Agency for Nature Conservation (BfN), relocated to the United Nations Premises in Bonn, where it has since resided together with other UN Agencies, such as: UN Volunteers (UNV), the Secretariat of the Framework Convention on Climate Change (UNFCCC) and the Secretariat of the Convention to Combat Desertification (UNCCD) (Introduction on the Conventions on Biodiversity Conservation, 2011). Bonn Convention Appendices I & II Appendix I – Endangered migratory species: Migratory species that have been categorized as being in danger of extinction throughout all or a significant proportion of their range are listed on Appendix I of the Convention. States strive towards strictly protecting these animals, conserving or restoring the habitats in which they live, and mitigating obstacles to migration and controlling other factors that might endanger them. Additional migratory species can be listed on Appendix I if a Party considers that they are endangered, and submits a proposal which meets the requirements of Resolution 1.5 (Bonn, 1985). Upon the recommendation of the Scientific Council, the Conference of the Parties (COP) would then decide whether to adopt the proposed in accordance with Art. XI. 14 Migratory species can be removed from Appendix I when the Conference of the Parties (COP) determines that there is either reliable evidence, including the best scientific evidence available, that the species is no longer endangered and that it is not likely to become endangered again. Appendix II – Migratory species conserved through Agreements: Migratory species that have an unfavourable conservation status or would benefit significantly from international co-operation organised by tailored agreements are listed in Appendix II of the Convention. For this reason, the Convention encourages the Range States to conclude global or regional Agreements for the conservation and management of individual species or, as is more often, of a group of species listed on Appendix II. In this respect, CMS acts as a framework convention from which independent instruments evolve. The Agreements may range from legally binding treaties to less formal instruments, such as Memoranda of Understanding, and can be adapted to the requirements of particular regions. The development of models tailored according to the conservation needs throughout the migratory range is a unique capacity of CMS. Such agreements have the great advantage that the Range States themselves decide on a tailored and structured action plan that includes the organization of joint research, monitoring activities and harmonisation of legislation (CMS website). 15 Mongolia and the Bonn Convention Brief introductions on conservation efforts undertaken for migratory wild species after Mongolia adopted the Convention: Like flora species, the fauna in Mongolia also includes the assemblages of the northern Siberian boreal coniferous forest, steppe, and Central Asian wild species. Local fauna species include at least 138 species of mammals, 495 species of birds, eight species of amphibians, 22 species of reptiles, 75 species of fish, and numerous species of invertebrates. Compared to other grasslands in the world, fauna species in the grasslands of Mongolia are wild and inhabit wilderness areas. There are 138 mammal species of eight orders of 22 families of 72 genera recorded in Mongolia. Among these species, there are 13 species of insectivore, 12 species of hymenoptera, six species of lagomorpha/leporidae, 69 species of rodents, 24 species of carnivores, two species of ungulates, one species of wild tylopoda, and 11 species of ungulates recorded (Biodiversity Action Plan of Mongolia, 2009). Due to human activities, some species have become extinct in the Mongolian grasslands. The Takhi (Equus przewalski) that was extinct in its natural habitat have been successfully re-introduced in three areas in the country. From the wild species that used to inhabit the country’s territory in early times (e.g. 1000 years ago), the red wolf (Cuon alpinus) and a sub-species of Saiga (Saiga tatarica tatarica) are already extinct. Currently, several species are threatened with extinction, however their populations are relatively higher compared to the populations in neighboring countries. For instance, the species e.g. the Mongolian gazelle (Procapra gutturosa), black-tailed gazelle (Gazella subgutturosa), Khulan (Equus hemionus), Mongolian saiga (S. borealis), Argali sheep (Ovis ammon), Bactrian camel (Camelus bactrianus ferus) are recorded in their largest populations in Mongolia. Carnivores such as the grey wolf (Canis lupus) are widely spread throughout the country, while the snow leopard (Uncia uncia) and other species have limited distribution. In recent years, the research and monitoring on game species abundantly distributed throughout the country’s vast territory has been intensively carried out for identification of their population sizes, hunting reserves, establishment of hunting quotas, and assessing populations of endangered mammals. For instance, in 1996-2010, there were studies on some game species e.g. the Mongolian gazelle (Procapra gutturosa) and Mongolian marmot (Marmota sibirica) and the endangered species listed in the Mongolian Red Book listed e.g. the Bactrian camel (Camelus bactrianus), Mongolian saiga (Saiga borealis), Argali sheep (Ovis ammon), Khulan (Equus hemionus), and Black-tailed gazelle (Gazella subgutturosa) and their resources and population sizes conducted within their natural habitats and distribution ranges with some depth reviews in some areas. Additionally, studies on over 50 game species in the country were conducted in 1980-1990 for identification and assessment of the species’ resources, distributions, populations, and annual quotas and their reports and materials are also available. There are some mammal species, whose populations have declined and habitats and distribution areas have been restricted, due to direct and indirect impacts of human activities and natural and climate factors. There are also quite many species, whose occurrence is recorded in few numbers within extremely limited areas or outer edges of their distributions and habitats are limited to some areas in Mongolia. Thus, the species in these situations would easily become extinct. The government of Mongolia pays particular attentions to the conservation of mammals namely endangered and wild game species. 16 The Mongolian Laws on Environmental Protection and Hunting (1995) provide legal basis of conservation, sustainable use, and restoration of mammals. Starting from the 1930s, hunting of about 10 species e.g. Takhi (Equus przewalskii), Saiga antelope (Saiga tatarica tatarica), Asian beaver (Castor fiber birulai), and Eurasian otter (Lutra lutra) has been legally banned. The environmental laws adopted in recent times pay significant considerations to the conservation of wild species. Moreover, some species e.g. Khulan, Takhi, and Asiatic wild dog (Cuon alpinus), Snow leopard (Uncia uncia), and Eurasian otter are recorded in the Red List of International Union for Conservation of Nature (IUCN). The species e.g. the Asiatic beaver, Gobi bear (Ursus arctos gobiensis), brown bear, snow leopard, Takhi (Equus przewalskii), Khulan (Equus hemionus), and musk deer (Moschus moschiferus) are listed in the Appendix I and the species e.g. the Asiatic wild dog, Gobi lynx Lynx lynx), Manul (Otocolobus manul), and European wild cat (Felis lubica) are listed in the Appendix 2 of Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES). The Mongolian Red Book was updated in 1997 and 30 species and sub-species of mammals were included in the Book under “rare” and “very rare” categories. Entire habitats and distribution areas of the species listed in the Mongolian Red Book e.g. Bactrian camel, Gobi bear, Takhi, Mongolian saiga, Siberian moose, wild boar (Sus scrofa), Asiatic beaver, and forest dormouse and partial or up to 70 per cent of habitats and distribution areas of the species e.g. the snow leopard, Khulan, Eurasian otter, musk deer, Argali sheep, and ibex have been included in the national Protected Area network (Biodiversity Action Plan of Mongolia, 2009). The Mongolian Laws on Environmental Protection and Hunting (1995) provide legal basis of conservation, sustainable use, and restoration of mammals. Starting from the 1930s, hunting of about 10 species e.g. Takhi, Mongolian saiga, beaver, and Eurasian otter has been legally banned. To date, a set of legislations on wildlife conservation are in force in the country. Additionally, the species e.g. Takhi, Khulan, red wolf, snow leopard and Eurasian otter are recorded in the Red List of IUCN, the species e.g. Takhi and Khulan in the Appendix I of CITES and the species e.g. Argali, musk deer, red wolf, lynx, saiga, Manul, and European wild cat in the Appendix 2 of CITES. Takhi and red wolf are extinct in their natural or wilderness habitats. Tthe Mongolian Red Book (1997) included 30 species and sub-species of endangered mammals under two categories. The Protected Area network in the country includes the entire habitats and distribution areas of the species e.g. Bactrian camel, Gobi bear, brown bear, Eurasian otter, and Takhi and some parts of the habitats of the migratory species e.g. the Mongolian gazelle, black-tailed gazelle, Khulan, musk deer, Argali sheep, and ibex. Conservation of birds within the country is also similar. However, populations of very many bird species have been reduced due to mortality outside the country. Birdlife International (2003) included four species of birds: Imperial eagle (Aquila heliaca), Lesser kestrel (Falco naumanni), Great bustard (Otis tarda), Hodgson’s stonechat (Saxicola insignis) recorded in the Mongolian grassland into potentially threatened species category. Breeding populations of these species are possibly found in Mongolia. In comparing to the neighboring countries, the grasslands in Mongolia provide more suitable habitats to big sized populations of a number of such bird species. For instance, the species e.g. the Black vulture (Aegypius monachus), Saker falcon (Falco cherrug), Henderson’s ground jay (Podicus hendersonii), and Macqueen’s bustard (Chlamedotis undulata) prefer dry steppe and desert steppe (Birdlife International, 2009). Riperian zones and swampy areas in Mongolia provide a home to water bird populations. For instance, there are some species of cranes. Birdlife International (2003) listed the worldwide bird important areas (seven), where the grasslands of Mongolia was included. The Dalmatian pelican’s sole breeding population in East Asia is recorded in 17 Lake Airag in the Western Mongolia. The swampy areas’ habitats in the country are vitally important to breeding populations of the globally endangered and nearly threatened species. For instance, they are important for the species e.g. the Swan goose (Anser cygniodеs), White-naped crane (Grus vipio), Relict gull (Larus relictus), Whiteheaded duck (Oxyura leucocephala) and the endangered species e.g. Siberian crane (G. leucogeranus) non-breeding population and potentially endangered species e.g. Hooded crane (G. monacha). Potentially endangered species, whose populations are limited (not so big) commonly occur in the grasslands of Mongolia. Although Mongolia is a landlocked country, it has several water or aquatic environments. The river system is blocked by dams and in some rivers support the fish species e.g. Taimen, whose body weights up to 99,8 kg, salmon, grayling, and pike, occur in some water bodies. The deep fresh water Lake Khovsgul located in the northern part of the country contains two per cent of the world’s fresh water. Lake Khovsgul, a home to the White-tailed sea eagle and Osprey, inflows into Lake Baikal just beyond the Russian border and also supports a number of interesting endemic species. The western part of Mongolia supports a depression of Great Lakes that supports several big sized fresh water, moderately salty, and salty lakes surrounded by high mountains in the basin. These lakes also provide a home to a number of water and shore birds including Dalmatian pelican, White spoonbill, Whooper swan, and goose. The north eastern part of Mongolia also supports some small sized lakes and rivers those are included into three Protected Areas. These lakes also provide a home to six species (including the White-naped, Hooded, and Siberian cranes) out of 15 crane species’ populations recorded in the world. The Mongolian Laws on Environmental Protection and Hunting (1995) provide basis of conservation, sustainable use, and restoration of mammals. Starting from the 1930s, hunting of about 10 species e.g. Takhi, Mongolian saiga, Beaver, and Eurasian otter has been legally banned. To date, the legislations on wildlife conservation are in force. Moreover, the species e.g. Takhi, Khulan, red dog, snow leopard, and Eurasian otter are recorded in the Red List of International Union for Conservation of Nature (IUCN). The species e.g. the Takhi and Khulan, are listed in the Appendix I and the species e.g. the Argali sheep, musk deer, red dog, lynx, saiga, Manul, and European wild cat are listed in the Appendix 2 of (CITES). Among these species, Takhi and red dog have been extinct in their natural habitats. The edition of Mongolian Red Book was updated in 1997 and 30 species and subspecies of mammals were included in the Book under “rare” and “very rare” categories. Entire habitats and distribution areas of the species listed in the Mongolian Red Book e.g. Bactrian camel, Gobi bear, Takhi, Mongolian saiga, Siberian moose, wild boar (Sus scrofa), Asiatic beaver, and forest dormouse or partial/up to 70 per cent of habitats and distribution areas of the species e.g. the snow leopard, Khulan, Eurasian otter, musk deer, Argali sheep, and ibex have been included in the national Protected Area network (Biodiversity Action Plan of Mongolia, 2009). National programmes on conservation and sustainable use of rare wildlife (plants and animals) in Mongolia e.g. a national programme on conservation of Saker falcon, a national programme on conservation of Snow leopard, and national programme on conservation of Argali sheep have been completed and implementation of some of them is underway. Brief introductions on conservation efforts undertaken for migratory wild species after Mongolia adopted the Convention а/ Actions and participation 18 The Parliament of Mongolia adopted the Convention on Migratory Species of Wild Animals on June 24, 1999.Upon signing the Convention, Mongolia first took part in the 6th meeting of its Contracting Parties. Wildlife in the country requires adequate conservation because 21 species including the Snow leopard, Bactrian camel, and Siberian crane, are recorded in Appendix I. Moreover, 177 out of 450 migratory species recorded in Mongolia are also recorded in the Appendix 2 to the Convention. Mongolia also signed three Memorandums of Understanding on the Siberian crane, Saiga antelope, and predator birds migrating and passing through the country on their migrations. In international practice, the countries not signed the Memorandum of Understanding and agreements are also allowed to join and take part the their interventions. The Mongolian Laws on Environmental Protection, Fauna, and Special Protected Areas, national programmes on conservation of Mongolian Saiga, Red Deer, Snow Leopard, and Argali sheep, and Biodiversity Action Plan of Mongolia are all being implemented in close integration with the Convention to fulfill the country’s commitments. On the 9th meeting of Contracting Parties to the Convention (held in Rome, Italy, December 1-5, 2008), the participants had a long discussion & disagreement over a proposal to include the Saker falcon in Appendix I and at the end of the long discussions they reached an agreement to make the decision to include the species in the Appendix I as its protection status is not changed ;however, the proposal was rejected at this meeting. The second regular meeting of the Parties signed the Memorandum of Understanding on Sustainable Use, Conservation, and Restoration of Saiga Antelope under the Bonn Convention framework was successfully organized in cooperation with the Participants of the meeting of the Parties signed the Memorandum of Understanding on Saiga Conservation, Ulaanbaatar, 2009 World Wide Fund for Nature in Ulaanbaatar on 7-10 September, 2010. The main output of this meeting was the development and approval of a midterm Saiga conservation programme for (2011-2015). The 10th meeting of COP was held in Bergen of Norway on 20-25 November, 2011. At the meeting, the focused areas related to Mongolia was a proposal by the European Union to include the Falcon saker in the Convention Appendix I and a proposal by Kazakhstan and Kyrgyzstan to include Argali sheep in Appendix 2, as well as a presentation of results of a research project on hurdles & obstacles to wildlife migration completed by the WWF Mongolia Programme office. As the discussion of proposal to include the Falcon saker in Appendix I faced big disagreements among the Parties, working group was established. At the end of seven meetings, the proposal was supported with an exception “to include all the species’ populations except for the population in Mongolia in the Appendix 1”. For the proposal to include Argali sheep in Appendix 2 was fully supported by the Parties. The research project on hurdles & obstacles to wildlife migration completed by the WWF Mongolia Programme office upgraded the reputation of Mongolia among the Parties. Acknowledged with the research efforts, the Parties recommended other Parties to conduct such research for migratory species e.g. tiger populations in India to fulfill commitments to the Convention. On the 10th meeting of COP, the Standing Committee to serve for the next three years were selected. From Asia, India and Pakistan were selected as its members and Mongolia and Iran were selected as alternative members. b/ Management and institutional structure: 19 In 2000, the Convention’s National Committee and scientific council were respectively established by the Directive of Minister of Nature and Environment and since then, representatives of the committee & council have been actively taking place in annual meetings of COP and Scientists Council. In 2010, the Steering Committee was re-appointed by the Directive А-88 of Minister of Nature & Environment as follows: D. Batbold, the Director of Foreign Relations & Cooperation department, was appointed as the Committee Chair, B. Sarantsetseg, the department officer, as the Committee Secretary, and B. Lkhagvasuren, N. Tseveenmyadag, D. Enkhbileg, & N. Batsaikhan as the Committee members. в/Projects and Programmes: The Government of Mongolia adopted the national programmes: e.g. national programme on Argali sheep conservation in 2002, national programme on conservation of Saker Falcon population in Mongolia in 2003, national programme on conservation and breeding of hunting or game fish species in 2008, national programme on Snow leopard in Mongolia approved by the Nature, Environment, and Tourism Minister’s Directive in 2005, and national programme on Mongolian Saiga conservation and national programme on Taimen conservation in 2007. Additionally, the State policy on ecology, Biodiversity Conservation Action Plan, national programmes on Protected Areas, Saker falcon, Argali sheep, Snow leopard, and Game fish species, and Saiga conservation have been developed and are being implemented. The national programme on conservation of Saker falcon population in Mongolia was implemented in 2003-2006 and 2006-2010. Under the national programme, distribution and resource of Saker falcon were identified in 2010. As per its findings, a total of 6,830 individuals were recorded in Mongolia. It provides for about 45 per cent of total Saker falcon populations in the world. Additionally, a project entitled “Building artificial nests for Saker Falcon” has been implemented for the last three years to improve nesting conditions, reduce the species mortality, and increase its population. Under this project, a total 5,000 nests were built and placed within distribution areas of the species in territories of 26 Soums of five Aimags in the steppe and Gobi regions. Supported this effort, the Ministry of Nature, Environment, and Tourism has been managing the monitoring on artificial nests, fledglings, and population size of the species starting from this year. As per the preliminary findings, a pair has 4-5 eggs in its naturally built nest and their fledging survival rate is 40-50%, but it would be improved to 70-80% as the artificial nests are built (Munkhtungalag, 2011). The Ministry of Nature, Environment, and Tourism and Environmental Agency in Abu Dhabi of United Arab Emirates signed a Memorandum of Understanding on Conservation of Predator Birds in Mongolia, as a part of the international programme, in 2007 to support the Saker falcon conservation and research, which is regarded as a important part of Saker falcon studies in Arabia. Under the Memorandum of Understanding, the project “Building artificial nests for Saker Falcon” has been successfully implemented for the last three years. By 2010, a total of 5,000 nests were built for the species. It was helpful to monitor the species population. Additionally, a documentary was produced to show the public the sustainable use of Saker Falcon and its evidences under the project interventions. The project “Building artificial nests for Saker Falcon” was supported by the MNET. The Minister of Nature, Environment, and Tourism, L. Gansukh, visited the United Arab Emirates at an invitation by Mr. Majiid Ali Mansuuri, the Director of Environmental Agency in Abu Dhabi of United Arab Emirates. During the visit, the parties agreed on the joint efforts to mobilize local communities into conservation 20 activities in the areas, where 5,000 artificial nests were built, provide them with rewards for their efforts, conduct public awareness on conservation, and train Mongolian junior specialists, officers, and biologists in order to make contributions in conservation of predator bird populations. The agreement will be implemented for five years with total funding equal to USD 2.4 million. The national programme on Snow leopards in Mongolia was implemented in 2005-2010. Under this programme, a project “Enterprise” was implemented to mobilize local communities into conservation of Snow leopard and its prey species. The project was jointly implemented by the International Snow Leopard Conservation Fund and 35 herder communities from 19 Soums of Uvs, Bayan-Ulgii, Khovd, Gobi-Altai, Umnugovi, Bayankhongor, and Uvurkhangai Aimags. A total of 450 female residents were involved into the project of making wool and cashmere products and living conditions of the project beneficiaries have improved by 80 per cent. It was one of the project’s success stories. The Institute of Biology under the Mongolian Academy of Sciences, and the International Snow Leopard Conservation jointly captured and put a satellite transmitter to a 5-6 year old snow leopard on Baga Bogd Mountain in Uvurkhangai Aimag. They also identified locations of the species every 7 hours with over 1100 points from August 21 to September 22, 2008. As per the data reported to the GPS and satellite images on locations of the captured individual (named Tuguldur), it was 87.6% (1080 records/ 1234 attempts) on GPS memory and only 13.6% (168/1234) on the satellite image. These findings show that the Snow leopard individuals wander throughout the mountain looking for their prey. It shows the species occur within huge areas so that the distribution areas and habitats to be conserved are quite big. 32 herder households of Tost Bagh of Gurvantes Soum of Umnugovi Aimag were involved in the livestock insurance project. In 2011, a total of 235 heads of livestock were caught by snow leopards and wolves (30 heads of livestock were killed by snow leopards and 205 heads by wolves). Under the project, the herder households lost their livestock were paid with MNT 11 million as compensation. WWF Mongolia Programme office implemented a programme “Buy sheep” among herder households residing nearby Turgen and Tsagaan Shuvuut Strictly Protected Areas and namely Jargalant and Bumbat Mountains in Altai Sayan region. Under the programme, three members of herder community “Umnud-Otor” were issued with six sheep. As informed by the herders, the negative (revengeful) attitude of local people to the Snow leopard has been reduced and eliminated as the programme was implemented. Although the herders, who lost their livestock due to attacks of predators, were compensated by sheep, the herders have well understood that they have to live in harmony with wild species namely the snow leopard inhabiting the mountains nearby as much as possible while taking preventive measures (Panda newsletter, 2011). d/Research Researches on migratory wild species are mainly carried out by the National Research Institution e.g. the Institute of Biology under the MAS in cooperation with the National University of Mongolia. In addition to these institutions, the WWF Mongolia Programme office, Snow Leopard Conservation Fund, hunting study center “Argali”, Wildlife Conservation Society and other research institutions (non-governmental organizations) also carry out their specific researches and studies on the species in their focus areas. 21 The Institute of Biology in cooperation with international researchers and explorers from other countries e.g. the USA, Japan, Germany, and Austria has been conducting research and monitoring on seasonal and annual migrations, breeding, and calving sites of the species e.g. Mongolian gazelle, Khulan, Bactrian camel, Argali sheep for collection of comprehensive ecological data for recent years by putting satellite image transmitting colors on selected individuals and using on-site monitoring devices. ©B.Lkhagvasuren Studies on Mongolian gazelle migrations were conducted in cooperation with researchers and experts from the USA within territories of Dornod and Sukhbaatar Aimags in 19982009. During the studies, satellite data transmitters were put on young and adult individuals for monitoring their migrations and movements. According to the research data, annual distribution and movement areas for adult individuals of Mongolian gazelle is 36,000 km2. It is the same as that in Serengeti National Park in Tanzania in Africa. This finding shows how big areas are needed for the species’ annual movements and migrations. The Institute of Biology in cooperation with researchers and scientists from the Universities of Tokyo and Tottori in Japan have been conducting monitoring on the Mongolian gazelle movements and migrations since 2002 as satellite image transmitters were put on 18 individuals in territories of Dornogovi and Umnugovi Aimags. As per their findings, the fences and mesh built along railways and State border are blocking the species seasonal movements and migrations and quite many individuals were lost or killed because of wire strands. 16 Khulan individuals in Khatanbulag Soum of Dornogovi Aimag were put with collars. According to the data on movements of four individuals, their active movements were recorded in August –September, January, and March with 30-45 km a week and 70 km the maximum. It was also recorded the railway and State border fences with wire strands blocked the species movements ©Kaczensky and migrations. From February 20 to March 15, 2010,a study on Snow leopards was conducted on Tsagaan Shuvuut Mountain located in the western part of Uvs Lake depression in People’s Republic of Tuva in the Russian Federation by the Mongolian-Russian joint expedition with supports of WWF Mongolia and Russian Programme offices in accordance with the agreement made between the Protected Area Administrations. During the field work, Tsagaan Shuvuut Mountain in Russia was almost entirely studied and 14 tracks, nine pieces of scrapes on trees, and 11 pieces of odornal SHUUREL were recorded and analyzed for genetic and DNA tests. Researchers also collected 46 pieces of waste for identification of individuals and sexes. ©Rodney J Based on the study and analysis findings, the core areas of Snow leopard were identified. As automatic photo cameras are placed in the areas for studying the species population compositions and biological and ecological characteristics. According to the preliminary findings, it has identified 8-10 individuals were inhabiting Tsagaan Shuvuut Mountain in Tuva. A long term monitoring programme on Snow leopard conservation is implemented on Tost Mountain range in Gurvantes Soum of Umnugovi Aimag. Under the programme, a total of 15 individuals were fitted with collars. As per the preliminary findings, the occupied areas of Snow leopard individuals are overlapped and male and female individuals occupy 60-400 sq.km area. An automatic photo camera was placed 22 and the individuals photographed were counted with their spots. As per its figures, there were about 20 individuals counted. According to the collared individuals’ prey analysis, 64 % fed on ibex, 25% on goats, 7 % on Argali, 2% on sheep, 1% on horse, 1% on camel. As per the waste analysis, 79% fed on ibex and 19.7% on domestic animals. Uvs Nuur Basin Special Protected Areas’ administration placed six automatic photo cameras (Bushnel, Reconyx) in Tsagaan Shuvuut SPA under the cooperation agreement with the Institute of Biology. The cameras were placed from May 20 to June 5, 2011 on Tsagaan Shuvuut SPA. Moreover, fresh wastes of Snow leopard were collected for genetic analysis and 50 Sherman traps were placed along the vertical zone of the mountain to identify species of small mammals. During the field works, collection and analysis of the samples needed for studies on Snow leopard ecology are still being continued. In 2011, the Russian and Mongolian researchers and scientists jointly produced a book on ecology, biology, and conservation of Bactrian camel listed in Appendix I to the Bonn Convention with a title “Two humped wild camel of Central Asia: habitats, biological characteristics, and conservation problems”. It is the first monograph work on the Bactrian Camel, the Central Asian’ endemic and very rare species in Mongolia (Jirnov et .al., 2011). WWF Mongolia Programme office implemented a research project “Hurdles in the migrations of ungulates in Mongolia” in 2011 with funding from Bonn Convention Secretariat. On the 10th meeting of the Convention Parties, Mongolia presented findings and results of a research project on Mongolian Saiga migration and impacts of infrastructural development on the species populations, a part of migratory ungulates in Mongolia. The research covered the migrations of four species: Khulan, Saiga antelope, and Mongolian and black-tailed gazelles. The research has also upgraded Mongolia’s reputation among the Parties. As a signing member of the Bonn Convention, Mongolia has its detailed national report developed and published by a non-governmental organization (as data and information necessary for development of the national report is collected). The development and publishing of the national report on the actions was supported by the UNDP Mongolia Country and WWF Mongolia Programme office. г/Training, meetings, & conferences: An international scientific research conference “Current state and future conservation” was organized by the Wildlife Conservation Society in 2003 for discussion of the migratory species that has remained in the largest populations in Central Asia. One of the decisions & recommendations from the conference was to develop the Mongolian gazelle conservation programme. International conference “Mongolian wildlife: conservation challenges and opportunities in 2010 and beyond” was organized by the MNET, WWF Mongolia Programme office, Institute of Biology, UNDP Mongolia, and Wildlife Conservation Society in Ulaanbaatar on 23-24 September. It was an important event addressed at wildlife research, conservation, and their current status and constraints as well as future actions. The recommendations from the conference were reflected in the national programme on conservation of rare and very rare wildlife species of Mongolia. IUCN/Equid specialist group’s meeting was held in Ulaanbaatar on September 26, 2009. The group meeting participants discussed the current status of Khulan and Takhi and constraints to their populations including the last winter’s dzud (heavy snow fall) impact on Takhi populations, and future actions. The meeting was chaired by Ms. Patricia Moelman (Tanzania), the Equid specialist group leader. The meeting recommendations 23 were also a part of the aforementioned conference. The second regular meeting of the Parties signed the Memorandum of Understanding on sustainable use, restoration, and conservation of Saiga antelope. It was held on 7-10 September, 2010 with support of WWF Mongolia. At the meeting, a midterm species conservation programme for 20112015 addressed the species conservation throughout its distribution areas was approved. The implementation of the midterm programme is monitored by the Saiga Conservation Alliance. The countries where the Saiga is distributed have to biannually report on the progress of conservation activities undertaken within the programme to the Saiga Conservation Alliance. As per its commitment, Mongolia reports on the species conservation efforts to the Alliance. International conference for development of strategic plan for Bactrian camel conservation was held in Khustai National Park in August, 2010. During the meeting, the current status and conservation of Bactrian camel populations were presented by representatives from each country, where the species occurs, for discussion and future strategic conservation action plans. At present the action plan is being translated into English and Mongolian. The action plan should be adopted by the Government of Mongolia and put into practice. Some of the activities proposed in the action plan are also reflected in the national programme on conservation of rare and very rare wildlife species in Mongolia. The conference on Siberian crane conservation was attended by P. Tsogtsaikhan, officer of Environmental and Natural Resource department of MNET in 2010. The conference on Saiga conservation held in Urumchi , People’ Republic of China, was attended by Enkhtuul, the CITES Secretary, in 2010. At initiative of WWF Mongolia Programme office, a meeting for improved conservation of Snow leopard was held in September, 2011 and it was attended by representatives of Mongolia, China, Russian Federation, Nepal, and India. On the meeting, the researchers and explorers from the “Pantera”, the Snow Leopard Conservancy, and the Institute of Biology, and representatives of Snow Leopard Conservation Foundation of Mongolia, and Khovd, Uvs, and Govi-Altai provinces. Following the meeting, the participants visited Tost Mountain in Umnugovi province, a site of Snow leopard conservation project for experience sharing. The 10th meeting of COP to the Bonn Convention was attended by D. Batbold, Chair of the Convention Board and Director of Foreign Relations department of MNET, and its Scientific Council meeting was attended by Dr. B. Lkhagvasuren, WWF Mongolia Programme office and the CMS Scientific Councilor for Mongolia. Red List of Mongolia’s Birds and Action Plan for Conservation of Birds in Mongolia were published in 2011. The Red List includes the birds recorded in Mongolia and the conservation action plan specified the status and future conservation actions for 36 bird species out of 476 bird species endemic to Mongolia. e/ Public awareness & promotional activities: Translations of 11 environmental Conventions and three Protocols, which Mongolia signed, were edited by the Ministry of Foreign Relations and Affairs and officially translated. The edited versions of the Conventions and Protocols were published in edition No: 9 of “Turiin Medeelel” (“State Information”) periodical dated March 31, 2010 and their copies were handed in to the respective agencies and institutions. One of the important awareness raising materials for the public is the publication of the Red List of mammals, birds, reptiles, amphibians, and fish in Mongolia and their conservation action plans that are helpful to raise public awareness on biodiversity in the 24 country. These publications specify categories of rare endemic (to Mongolia) species in regions within the country according to the IUCN categories, characteristics of each species listed, reasons of their rarities, distributions and population sizes in the world and regional levels, their protection status, and future conservation actions. These publications are an important reference on the species for decision makers and other relevant institutions and organizations. Introduction on international Conventions on biodiversity has been produced with the support of WWF Mongolia Programme office for the public. A pamphlet “Gobi King” on globally endangered transboundary Bactrian camel written in English for children was translated by Dr. B. Lkhagvasuren into Mongolian and distributed to the MNET and the public. The Mongolian Snow Leopard Conservation Foundation and the International Snow Leopard Conservation Foundation jointly implemented a public awareness programme of Frankenberg for local herders in 2011–2012. Under the programme, lectures and discussions on the species conservation and ecological importance were organized for local residents of the areas where Snow leopards inhabit. With the cooperation of the British Broadcasting Corporation (BBC), the foundations prepared a 10 minute programme on Snow Leopard conservation (“Irves Enterprise”) in November, 2011. It was sent to the BBC “World Challenge“ documentary contest and won the first place in the contest, where 12 documentaries and programmes were shortlisted out of the documentaries and programmes sent by many countries in the world. It shows that the Snow Leopard conservation in the country is being highly appreciated by international communities. 25 BRIEF DESCRIPTIONS OF THE WILDLIFE SPECIES LISTED IN APPENDIX TO THE BONN CONVENTION Mammals in Appendix I: Bactrian Camel (Camelus bactrianus ferus) Two humped camel or Bactrian Camel, whose occurrence is only recorded in Mongolia and China in the world, has a populationofs about 450-500 individuals in Mongolia in four areas according to the recent researches and studies (Adiya et.al., 2010). The International Union for Conservation of Nature (IUCN) included the species into the category ”critically endangered” or A3de and À4ade. As per the regional assessment, the species is listed in the category “nearly endangered” С1 (Clark et al., 2005). Hunting of Bactrian Camel has been legally banned since the 1930s. It was protected in 1958 and its core distribution area was included in Great Gobi Strictly Protected Area (SPA) in 1975. From Great Gobi SPA, 22 calves were captured and raised them in Bayan-tooroi area in Govi-Altai province in 1987-1992. However, only 13 individuals are left because of inadequate understanding and skills in taking care of the species and management. National researchers consider that one of the reasons to become rare is crossbreeding with domestic camels. There are no comprehensive studies on cross-bred individuals, but local herders inform that their camels have become conciliatory with the wild camels. It was often seen that domestic camels moved and grazed in part “A” of Great Gobi SPA. It provides a basis of outbreak of contractible diseases and crossbreeding (Walzer, Kaczensky, 2005). Distributions and locations of Bactrian camel are likely to be influenced by human activities and natural resource extractions (e.g. gold mining) and environmental deterioration in the future. In China, rivers are getting polluted with cyanide as sodium cyanide is used for iron ore concentrates in gold mines (Hare, 2006). Fences along the Chinese and Mongolian border also hinder migration and movements of Bactrian camel and hold back potential genetic cross-breeding with the species populations in China. It is indefinite whether the changes to oasis environment e.g. increasing dryness are being resulted from human activities and whether water bodies are lost due to natural phenomena. One of the causes reducing the Bactrian camel’ small populations is that of wolf attacks on the wild camel herds, particularly on young individuals or calves (M. Stubbe, personal commentary). The species is legally protected as it is included in the list of very rare wild species in Article 7.1 of the Mongolian Law on Fauna (2000) (Badam, Ariunzul, 2005). Hunting of Bactrian camel has been legally banned since the 1930s and the species is included in the list of very rare wild species in the Law on Hunting (1995) (Ministry of Nature and Environment, 1996). The species is also recorded in the category of very rare species in the second edition of the Mongolian Red Book (Shagdarsuren et.al., 1987; Shiirevdamba et.al., 1997). The species is listed in Appendix I to the Bonn Convention. Distribution areas of Bactrian camel are entirely included in the Protected Area network in the country. The national programme on Bactrian Camel Conservation has been developed and its discussion is underway. As the programme is approved and put in practice, the conservation status and management will be radically improved. At the initiative of the 26 Government of Mongolia, a project for Bactrian camel was successfully implemented with UNDP/GEF funding in 2004-2007. Snow leopard (Uncia uncia) The Snow leopard (Uncia uncia Schreber, 1776) occurs in 12 countries (e.g. Afghanistan, Bhutan, China, Mongolia, India, Kazakhstan, Kyrgystan, Nepal, Pakistan, Russian Federation, Tajikistan, and Uzbekistan) with limited distribution. it’s the populations are 4500- 7000. The snow leopard is recorded in the Red Book of Mongolia, Red List of IUCN, Appendix to the CITES, and Appendix I to the Bonn Convention and its hunting is banned. The species is listed in category of “endangered” or C2a(i) of IUCN (Clark et al., 2005). To protect the species, the countries cooperate through establishment of transboundary Protected Areas. The species populations are commonly found in the areas that are in natural or untouched conditions. There are approximately 700-1200 individuals recorded within 80.0-100.0 thousand sq. km areas of Mongol Altai, Govi-Altai, Khangai, Khan Khukhii, Khovsgul, Kharkhiraa, Turgen, and Tsagaan Shuvuut Mountain ranges and continued low mountains of South Altai Gobi located in 107 Soums of 10 provinces in the country. About 20 per cent of habitats of Snow leopard populations in Mongolia are included in the national Protected Area network. According to the Snow leopard researchers, 13.022.0 per cent of world populations of Snow leopard occurs in Mongolia (McCarty, 2000). There were 500-1,000 individuals in the Snow leopard populations in Mongolia in 2000 (McCarthy, Chapron, 2003). Habitats and distribution areas of Snow Leopards overlap with habitats of Ibex, one of its main prey species. The species also feeds on Argali sheep, marmot, rabbit, rodents, and birds such as Snow cock and rock partridge. When these prey species become rare within its habitat, the Snow leopard often attack domestic livestock. The snow leopard is recorded in the list of very rare wildlife species in Mongolia. Individuals who illegally hunt the species are imposed with criminal liabilities. The Mongolian Law prohibits to sell and buy the items made of snow leopard skin and other parts. However, the species is illegally hunted for smuggling its skin and bones for traditional medicine to China. Additionally, its meat is used for traditional medicine. One meter of snow leopard skin traded in Mongolia and China is at least USD 250 (Wingard, Zahler, 2006). One of the causes reducing the species populations in the country is the lack of prey species (particularly, ungulates) within their habitats. Some individuals that attack livestock are shot by herders. The species population is getting reduced due to illegal hunting for smuggling to other countries. National and international research institutions jointly carry out studies, analysis, and conservation efforts of Snow leopard in the country. WWF Mongolia Programme office implemented a project of Snow leopard conservation in Western Mongolia. Under the project, some heads of livestock were provided to the herders, who lost their livestock because of snow leopard attacks and campaigns on the species conservation were conducted. The similar projects and programmes were implemented by the Institute of Biology and International Snow Leopard Conservation Foundation on Small Bogd 27 Mountain in Uvurkhangai province and by the Mongolian center for Snow Leopard Conservation jointly with the US Pantera International on Tost Mountain in Umnugovi province. Under the projects and programmes, collars were put on snow leopard individuals and their seasonal movements were monitored. In addition to data on seasonal movements, they collected data on the species habitats and distribution areas that are important for future conservation management. Birds There are 21 bird species included in Appendix I to the Bonn Convention. As an example, we have cited below a brief description on the Oriental white stork in this report. Oriental white stork (Ciconia boyciana) The International Union for Conservation of Nature (IUCN) has included the species in the category “endangered” or C2a(i) as per its assessment. No regional assessment has been made for the species (Gombobaatar et al., 2011) The species occurs in Ulz River, Buir Lake and Khalkh River valleys in Mongolia during its spring and autumn migrations. There were 1000-2,499 individuals recorded within 474,000 sq.km area, but its population size in Mongolia has not defined (Gombobaatar et al., 2011). Gombobaatar © The species is recorded as a “rare” species in the Mongolian Red Book (1997) and its hunting has been banned since 1995. The species is also listed in Appendix I to the CITES and Appendix I to the Bonn Convention It is also recorded in the list of rare birds in Mongolia. 22.4 per cent of its habitats and distribution areas have been included in the current Protected Area network (Gombobaatar et al., 2011). Mammals in Appendix II: Mongolian gazelle (Procapra gutturosa) The ungulate that remains at its largest numbers in Central Asia is the Mongolian gazelle. (B. Lkhagvasuren, 2000). The Mongolian gazelle used to migrate within 750,000 km2 of all steppes, desert steppe, and mountain steppe in Mongolia in the 1950s (Bannikov, 1954). Currently, its distribution areas have been reduced to 500,000km2. Migration of the large herds from the east to the west within the country has been blocked by Ulaanbaatar- Zamyn Uud. Ito T. © As the species populations were fragmented by the railway, the populations to the west of railway have been badly affected by droughts and dzud (heavy snow falls) and hunting and consequently most of the population has been lost and seen in few numbers in some places (Lkhagvasuren, Milner-Gulland, 1998). One of the factors reducing its populations is that numbers of individuals illegally hunting who always override the annual quotas for hunting.The species is illegally harvested in large numbers (Lkhagvasuren, Milner-Gulland, 1998). Milner-Gulland, Lkhagvasuren (1998) presumed hunting quota a year would be 60,000 individuals from the population with one million individuals. However, the individuals hunted has been exceeded by over 300 per cent (Wingard, Zahler, 2006). In Eastern Mongolia, about 70,000 Mongolian gazelles were harvested in the winter of 1977(Sokolov, Lushchekina, 1997), but 250,000 individuals were illegally harvested in 2004 (Wingard, Zahler, 2006). Binary fence along Ulaanbaatar- Beijing 28 railway has divided the core populations in Eastern Mongolia. It makes the population status worse and fragmented. Wire mesh along the Russian-Mongolian and ChinaMongolian borders hold back access to better rangeland during their annual and seasonal migrations (Ito et al., 2005). One of the causes reducing the species populations is the increasing hunting of Mongolian gazelle in some areas (particularly in the areas, where oil is extracted)as a meat supply. In addition to this, the causes of the species decline is competition with herders and outbreak of contagious diseases such as hoof and mouth disease especially risky in the areas where human and livestock are highly concentrated (Schaller, Lkhagvasuren, 1998; Campos-Arceiz et.al., 2004). In some winters with dzud (heavy snow fall) the species is lost in large numbers. The species hunting has been handled under control and annual hunting quotas for business purposes have been set at a regional level since 1932. Its hunting season has been set from September 1 to December 1. The Ministry of Nature and Environment has banned the species hunting for commercial purposes since 2000 (MNE, 2000). The Law on Hunting (1995) banned hunting of Mongolian gazelle by using guns and chasing by vehicle. In the event of illegal hunting, the violators will be fined with the domestic currency equal to USD 30-40 per head hunted. Approximately, eight per cent of the species habitats and distribution areas are included in the current Protected Area network. Mongolian Saiga (Saiga borealis) There are two fragmented populations of the species in only 20 per cent of the former distribution areas of the species in the western region of the country. The majority (90%) of one population occurs in a 2,000 km2 of distributed areas in Shargiin Gobi, the desert valley in the north of Govi-Altai Mountain range. Located at 200 km distance from Shargiin population, other population occurs in about 200 km2 in sand dunes located in the south of Khar Us Lake (Dulamtseren, Amgalan, 1995). Few individuals used to occur in Khuisiin Gobi and Khuren steppe in the Great Lakes’ depression, but the species occur permanently in these aforementioned areas (WWF, 2010). Total distribution area of the species is approximately 130,00 km2. At the initiative of the WWF Mongolia Programme office to re-introduce and increase populations of Saiga within its natural habitats and distribution areas, a project “Conservation of Saiga in Great Lakes’ Depression” was implemented with funding of Euro 500,000 from MABA Foundation in Switzerland in 2007-2010. As the project was implemented, the Saiga population was increased as per the project data. Under the project intervention, community based organizations were established within the project sites, anti-poaching unit “Irves-3” was established in Govi-Altai province, 3-year public awareness programme on prevention from illegal hunting and trade was developed and implemented, and collars were put on six adults and 40 baby individuals for monitoring their movements and migrations. WWF Mongolia Programme office is implementing the programme “BioFund”, a database on rare and endangered wildlife (including Saiga) distributions, locations, populations, and other relevant data and the “Irves” database, where illegal hunting related data and evidences are collected. The species populations are quite limited and vulnerable to natural disasters (Lkhagvasuren et.al., 2001). Compared to other species, its hunting is relatively lower in Mongolia, but hunting is a threat to the populations with few individuals. Illegal hunting 29 takes place for males’ horns as they are used for traditional medicine. It affects not only overall populations, but also the gender balance among the populations (WWF, 2010). Some researchers regard the reduction in species populations has indirectly resulted from habitat loss and deterioration by the drastic increase in domestic livestock. Domestic livestock creates competition for grazing and water within the species habitat, but it necessary to conduct comprehensive studies on this concern. Another threat to the species populations are the contagious diseases and parasites (e.g. Pallasiomyia antilopum) from domestic livestock (Dulamtseren, Amgalan, 1995; Zahler et.al., 2004). The species is recorded in the CITES Appendix II (UNEP-WCMC, 2006). Two sub-species are recorded in a category “very rare” in Article 7.1 of the Mongolian Law on Fauna (2000) (Badam, Ariunzul, 2005). Since 1930, its hunting has been banned and the species is included in a category “very rare” species in the Mongolian Law on Hunting (1995) (MNE, 1996). Two sub-species are included in the category “very rare” species in the second edition of the Mongolian Red Book (Shagdarsuren et.al., 1987; Shiirevdamba et.al., 1997). Approximately 24 per cent of Mongolian saiga habitats and distribution areas are included in the current Protected Area network in the country. Khulan (Equus hemionus) Khulan is recorded in limited numbers in few countries of Arabia and Asia Ito © including Israel [re-introduced], Saudi Arabia [re-introduced], Iran, Kazakhstan [reintroduced], Turkmenistan [the population being re-introduced], Uzbekistan [reintroduced], China (the northern part of Xinjiang province), India, and Mongolia (Feh íàð, 2002). However, the species has been extinct in the Near East, namely in the Arabian peninsula, Asia Minor, and the northern part of India. The International Union for Conservation of Nature (IUCN) includes the E. hemionus in the category “vulnerable, A3bcd and C1 and the E. h. hemionus, E. h. luteus in the category “vulnerable”, C1. Its population had 19,000-20,000 individuals in 2003 (Lkhagvasuren, 2007) and its populations have been reduced due to uncontrolled hunting, environmental degradation, and reduced breeding rates among herds. Over 3,000 individuals were illegally hunted a year (Wingard, Zahler, 2006). As per this finding, the species populations were reduced by five per cent a year and by over 60 per cent within last two decades. According to the inventories on ungulates in the steppe region (2009), about 13,000-15,000 individuals were recorded (Institute of Biology, 2009). It shows that the intensive mining operations taking place in the southern Gobi region in recent years lead to a drastic loss of the species population and their habitats. In some areas, the species is illegally hunted for smuggling of its skin and meat (Duncan, 1992; Stubbe íàð, 2005b). The species habitats are getting lost and deteriorated due to overgrazing (specific data is required) as domestic livestock is increased, extensive use of natural resources (e.g. mining), human settlements (near oasis and water bodies). Wire mesh fences along Ulaanbaatar-Beijing railway and Chinese-Mongolian border have fragmented the species habitats and hold movements and migration within its natural habitats (Kaczensky et al., 2009). The species was included the Appendix II to the Bonn Convention in 2002. The E. hemionus is included in the CITES Appendix II and the E. h. hemionus, E. h.luteus is in Appendix I. Khulan is included in the category “rare” species in the revised Mongolian Law on Fauna (2000) (by the Government Resolution No: 264, 2001) (Badam, Ariunzull, 2005) and in the category of “rare” in the Mongolian Law on Hunting (1995) 30 (MNE, 1996). Its hunting has been banned since 1953 (Shiirevdamba et.al., 1997). The Khulan was included in the category of “rare” in the second edition of Mongolian Red Bool (Shagdarsuren et.al., 1987; Shiirevdamba et.al., 1997). Approximately 29 per cent of Khulan distribution area is included in the current Protected Area network. To protect the species, the Government established part “B” of Small Gobi Strictly Protected Area (Zuungaryn Gobi) and Zagiin Us (Saxual stand) Nature Reserve (Northern Gobi) in 1999 (Feh et.al., 2002). Black-tailed gazelle (Gazella subgutturosa) The species is distributed in 20 countries of Central Asia and Arabia. Mongolia supports relatively bigger and healthier populations distributed within vast areas, but with low density. Currently, it abundantly occurs in the Great Lakes Depression, The Valley of the Lakes, .Zuungaryn Gobi, Altai Uvur Gobi, Eastern Gobi, and Alshani Gobi (Bannikov, 1954; Sokolov, Orlov, 1980; Amgalan, 1984, 1986; Lkhagvasuren et,al., B. Lkhagvasuren© 1999; Lhagvasuren et al., 2001). As per the International Union for Conservation of Nature (IUCN) assessment, the species is in the category “vulnerable” and A2ad and as per the regional assessment, it is in a category “vulnerable”, A3cde (Clark et al., 2005). The species population in Mongolia was reduced by 30 per cent from 1940 to 1960 (Lkhagvasuren et.al., 2001). In the 1990s, the population size was about 60,000 individuals (Amgalan, 1995) as per the steppe ungulate inventories in 2009 (Institute of Biology, 2009) it was reduced by 5 times at about 12,000 individuals. The main causes of reduced population were unregulated and uncontrolled hunting and other factors e.g. environmental degradation, competition for resources, and other intentional human activities. In addition to the permitted hunting, the species is illegally hunted for its meat. Many researchers identify the mining operations intensively undertaken in the South Gobi directly and indirectly lead to the species habitat fragmentation and reduced population (Lkhagvasuren et al., 2011). The species was recorded in the Bonn Convention Appendix II in 2002. The species was recorded in a category “rare” species in the Mongolian Law on Hunting (1995) (MNE, 1996). The species was also recorded in a category of “rare” as per the Mongolian Law on Fauna (2000) and Government Resolution (¹264, 2001) (Badam, Ariunzul, 2005). The species is also recorded in the category of “rare” species in the second edition of Mongolian Red Book (Shagdarsuren et.al., 1987; Shiirevdamba et.al., 1997). Approximately 15 of Black-tailed gazelle habitats and distribution areas is included in the current Protected Area network (Amgalan, 2000). Argali sheep (Ovis ammon) Argali sheep, which is well recognized with its big body and horns, occurs in 12 countries in Asia in the world. There were two sub-species: Altai Argali sheep (Ovis ammom ammon) and Gobi Argali sheep (Ovis ammom darwini) occurring in Mongolia. However, researchers identify there is one species of Argali sheep (Ovis ammom ammon) in Mongolia based on genetic analysis (Tserenbataa 2003; Tserenbataa et al., 2004). As per the IUCN assessment, it is included in a category “vulnerable” or А2cde. It also includes Altai Argali sheep in a category “vulnerable” or A2cde and C1 and the Gobi Argali sheep in a category “endangered” С1 (Clark et al., 2005). 23.4 per cent of the species habitats and distribution areas is in the current Protected Area network in the country. 31 A national programme on Argali sheep conservation was approved by the Government Resolution in 2002. To protect the species population growth and habitats, 11.3 thousand sq.km area of Myangan Ugalz Mountain in Uvs Aimag was designated under the State protection by the Parliament Resolution No: 39 in 2002. To improve conservation management of Khukh Serkh Nuruu SPA including efficient biotechnical measures, a park administration was set up in Deluun Soum of Bayan-Ulgii province. The main constraint and threat to Argali sheep is illegal hunting including hunting of the species by foreign hunters with special permits (Amgalanbaatar et al., 2002b). The main causes of the population decrease include the droughts and dzud (heavy snow falls) that frequently occur, overlapped grazing areas with domestic animals, habitat restriction and even loss of some parts of its historical distribution areas (Reading et al., 1997; 2003; 2005; Wingard, 2005). Its hunting has been legally banned since 1953. The species was included in a category “rare” in the Mongolian Law on Hunting (1995) and the CITES Appendix II. It was included in the Appendix II to the Bonn Convention on the 10th meeting of COP to the Convention held in Bergen of Norway in November, 2012. The species is recorded in a category “rare” in the Mongolian Red Book. (Shagdarsuren et.al., 1987; Shiirevdamba et.al., 1997). Approximately 14% of the species habitat and distribution area is included in the current Protected Area network. The population in Mongolia was 60,000 individuals in the middle of 1980 (Institute of Biology, 1985), but it was 18,000-20,000 individuals in 2009 (Institute of Biology, 2010). The species population in the country has been reduced by three times during the last two decades. National and international research institutions jointly conduct studies on the species. For instance, researchers of Biological Institute in cooperation with researchers from the USA are implementing projects in Ikh Nart Nature Reserve in Dornogovi province and Altai mountain range a site of WWF Programme office. Birds: 177 bird species in Mongolia are listed in the Appendix II to the Bonn Convention. As an example, we have cited below a brief description on Greylag goose in this report. Greylag goose (Anser anser) It is a migratory bird occurring in most major rivers and lakes in the country. The species annually arrives in the country in mid April and the beginning of May and build their nests in rivers’ and lakes’ valleys for nesting and summering. The species occurs in a number of countries in the world its world population is about one million individuals, but the population size in the country has not yet been defined. (Gombobaatar, 2011). S. Gombobaatar© Traditionally, Mongolians do not hunt birds while respecting and revering them. Thus, direct human impacts on the species population are relatively less, but other factors e.g. environmental degradation, farming or cultivation, infrastructural development, and particularly mining operations lead to the species habitat fragmentation and decreased populations (Gombobaatar, 2011). Approximately eight per cent of its habitats and distribution areas is in the current Protected Area network (Gombobaatar, 2011) and the wetlands, where the species occurs, are recorded in the RAMSAR Convention Appendix. 32 Fish Two species of fish in Mongolia are recorded in the Bonn Convention Appendix II. We have cited below a brief description on Siberian sturgeons in this report. Siberian sturgeons (Acipenser baerii) As per the IUCN assessment, the species is recorded in the category “endangered”A2bcd+ 4bcd ver 3.1 and as per the regional assessment, it is included in a category “near threatened” B2ab (iii,v). Its distribution area is less than 10 km. It spawns in three areas (two in Selenge River and one is in Orkhon River). Its distribution area is limited so illegal fishing is a main threat to the population. Lucas Jurek© Its habitats are polluted with sediments and other waste materials produced by gold mining and the species population has been drastically reduced because of illegal fishing of its breeding individuals. Main threats are illegal fishing for trading and habitat pollutions resulted from non-organic waste from urban or settlement areas and different sized (small and big mining company operations) mining operations. Due to adverse impacts of gold mining operations, changes are made to its habitats e.g. river regimes and shapes are changed and sludge or thick clay accumulates at the river bottoms and. Consequently, the species faces and has faced a lack of pollution free environment and habitat. The species is included in the CITES Appendix II in 1998 and Bonn Convention Appendix II. The species is under a category “rare” in both the Mongolian Law on Fauna or the Mongolian Red Book. 33 DECISIONS OF MEETINGS OF THE COP TO THE CONVENTION AND THEIR FOLLOW UP ACTIONS IN MONGOLIA Since 1999, when Mongolia signed the Convention: Decisions those are pertinent to Mongolia: Follow-up actions decisions: of the Decision 6.5. Cape As per decision 4.1 of the meeting Report was sent in a timely manner; held in Nairobi in 1994, to remind the Town, 1999 COP to timely submit their reports to National Report the Convention before the meetings of COP to contribute conclusions; Bonn, To carry out joint actions necessary for the conservation of the species: a mammal species of terrestrial land: Snow leopard A broad range of joint efforts including projects and programmes for Snow leopard conservation are being undertaken, National programme on Snow leopard was successfully implemented in 20042010. Decision 7.2. Bonn, Recommend the COP compliance to the instructions to reflect the 2002 biodiversity related issues in the Impact assessment Environmental impact assessment legislation and the Environmental strategic assessment approved by the meeting VI/7 of the COP to the Convention on Biodiversity; A statement on Environmental impact assessment is specifically included in the Law on Environmental Protection; Mobilize the COP to the Convention, non-member and observer countries, and other partners into cooperative actions to support sustainable management of predator birds and owls; for instance, (a) Protect important breeding sites and take mitigation measures to reduce and eliminate the hurdles & obstacles to their migrations and movements; (c) Monitor & track on shooting, poisoning, and the taking away of their eggs; (d) Conduct promotions & public awareness on behaviors, living patterns, constraints & challenges to the bird populations and their conservation; (e) Conduct monitoring & assessment A database on over 10 predator birds and their movements and conservation in Mongolia was established; Breeding sites of most of the predator birds are included in the national Protected Area network to certain extents; A project on reduction of mortality of steppe predator birds hit on high tension lines in Mongolia was implemented in 2008-2011; Laws on Fauna and Hunting bans to shoot and take away eggs of predator birds and monitoring is conducted through a network of Protected Area administrations, Aimag and Soum environmental institutions’ cooperation; Research institutions and non- Decision 7.1. 2002 Cooperation Decision 8.12. Nairobi, 2005 Predator birds 34 at regional level to identify governmental organizations actively population trends and conduct carry out awareness activities on necessary studies on the species; conservation of some predator birds and better understanding on constraints and threats to the birds for the public; To identify and analyze predator birds’ population trends, monitoring and assessment on populations were conducted at regional level and conservation action plan for birds recorded in the Red List was developed in 2011. Decision 8.27. Nairobi, Develop a comprehensive action plan 2005 Avian influenza for combating with HPAI and other animal contagious diseases at national and international levels through participation of researchers of wetland birds and other wildlife species, public health, specialists and experts studying contagious diseases from animals to humans e.g. the specialist & experts from veterinarian, agricultural, bacterial studies, and medical sectors; Analyze and share database and analysis findings on migratory routes, flyways, and dynamics of predator bird populations with stakeholders and partners in order to improve conservation efforts; Necessary emergency actions are timely undertaken in the events of the discovery of contagious disease symptoms through participation of researchers of wetland birds and other wildlife species, public health, specialists and experts studying contagious diseases from animals to humans e.g. the specialist & experts from veterinarian, agricultural, bacterial studies, and medical sectors as per the comprehensive action plan; National ornithologists and other researchers jointly do analysis in database findings to identify and assess migratory routes, flyways, and dynamics of predator bird populations with the partners e.g. FAO; Put in force a Memorandum of Understanding on Saiga conservation, re-introduction, and sustainable use as it has been signed by respective countries (three); Encourage non-member countries to actively take part in enforcement of proposed actions as inviting them to join the agreements & negations; Mammals of Central Asian terrestrial land: (ii) Call for observers-countries and other parties interested to take part in As Mongolia signed the Memorandum of Understanding in 2010. Efforts for Saiga conservation efforts are being undertaken with a broad range; Decision 9.2. Rome, 2008 Prioritized issues of the Bonn Convention agreed by its COP 35 Since its start, Mongolia has been taking place actively in the cooperation. It initiated to conduct the assessment of constraints and hurdles to the Mongolian gazelle and other migratory ungulates with funding from the Convention the Convention activities and support in drafting & signing of memorandums of understanding and other direct and indirect documents; (iii) Support and cooperate with nonmember countries in terms of conservation of Mongolian gazelle as per the 14th Scientific Council meeting of the Convention; (iv) Advise and assist the countries, where the Mongolian gazelle is distributed, in development of their action plans for the species conservation and improvement of cooperative efforts for conservation of the threatened species; Decision 9.4. National reports their future Secretariat and reported about the assessment findings to the Convention Scientific Council and the 10th meeting of the COP. The Parties that have not submitted Reports were & their national reports for 2005-2008 deadline; need to send them by December 31, 2008; sent within the Integrate the wildlife (animals & plants), domestic animal, human, and ecosystem health issues into the following aspects: А. Action plans for emergency situations; B. Monitoring, assessments, & observations; C. Responsive actions to be undertaken during outbreaks of pandemic and contagious diseases and mortalities; D. Capacity building actions; Decision X.21 of Ramsar Convention and its recommendations to the COP following up the instructions addressed at reduction and elimination of H5N1 avian influenza outbreaks; Responsive actions are timely taken in accordance with the action plans for emergency situations and outbreaks of wildlife contagious diseases (e.g. outbreak of foot and mouth in 2010) and the instructions of Ramsar Decision and H5N1 avian flu outbreak mitigation are followed up; 3. Recommend the Parties identifying Decision 9.12. Strategy for capacity the prioritized areas of researches based on the most reliable evidences building and data and improving capacities while focusing on the prioritized concerns to migratory wildlife; National and international researchers cooperate in analysis of seasonal movements of migratory species e.g. Mongolian gazelle, Khulan, and Argali sheep through putting satellite image transmitters (collars) on individuals and Decision 9.8. Take preventive actions against the contagious diseases such as H5N1 avian influenza frequently outbreak among migratory birds; 36 identifying and assessing the hurdles to their seasonal movements, migrations, and habitat conservation and reflection of analysis findings in future management plans; As per the clause 4 of section VII of Mongolia pays its contributions in a Decision 9.14. Finance & the Convention, The Conference of timely manner; administrative issues the Parties shall make their contributions to the Convention by the end of March of each year. If necessary, the Parties may claim from the Secretariat an invoice of three year’s contributions; 7. If agreed, the Parties may pay their contributions in three equal portions; Decision 9.20 Saker falcon Require the Parties to provide their supports to the seminar on the conservation and needs of Saker falcon conservation to be held in the United Arab Emirate in 2009; Request the Parties to accept and support the research programme initiated by the Saud Arab to reassess the species conservation status; Recommend the Parties proposing to list the species in the Appendix I other than the species, whose conservation is apparently upgraded and those are no longer regarded as vulnerable, endangered, and threatened species; Under the task, a project to put radio and satellite transmitters on Saker falcon individuals for monitoring their migrations and build artificial nests was implemented in Mongolia. A total of 150 artificial nests were built. Monitored migration of 10 individuals, it identified that the individuals leave from Mongolia and spend their winters in the north west of China and on mountains of Khukh Lake and some adult individuals spend their winter in Mongolia. Monitoring on their food & prey, habitats and breeding was conducted; Decision 10.03 Bergen, 2011 Role of ecological chain in conservation of migratory species Call for the COP and the Parties signed Memorandum of Understanding to use and apply a network or chain tool for implementation of the Convention document, proposals, and initiatives on migratory wild species; Identify migratory terrestrial and water bird important areas that include the ecologically important areas e.g. breeding sites and nonbreeding areas e.g. stopover sites (for resting & feeding) and mobilize the COP and observers-Parties to produce the map and patterns The Memorandum of Understanding on Saiga Conservation was signed and Mongolian Saiga movement and migration routes were designated into a Nature Reserve (Sharga Mankhan NR). Breeding and calving sites of migratory species e.g. Bactrian camel, Mongolian gazelle, and Khulan have been entirely and partially designated under protection and included in the national Protected Area network. Joint studies on trans-boundary migratory species e.g. Bactrian 37 systematically relationships; Decision 10.07 Activity outputs communications (Expected outputs the actions communications 2012-2014) showing their camel, Mongolian gazelle, and Argali sheep were conducted with neighboring countries (China and Russia) and a trans-boundary Protected area was established; Recommend the Parties raising and and donating financial and other physical contributions to implement efficient of campaigns; and Set the frequency of the campaign in for accordance with the recommendations in CMS/StC37/20; Maintain records and support the activities organized by the envoys of the Convention on Migratory Species; Report to the Secretariat if an envoy(s) took part in the activities and events for migratory species conservation; Mongolia actively takes place in the activities and events for conservation of Siberian crane and Saiga as it signed the Memorandum of Understanding on the species’ conservation and sends it representatives to international workshops and conferences on Saker falcon conservation for making inputs into their decisions and recommendations; Decision 10.10. Instructions and policy coordinations with regard to conservation of migratory flyways; 6. Recommend the Parties dealing with the issues to designate birds’ stopover points under protection and carry out necessary coordination tasks; 7. Call for the Parties to support the development of internationally bird important areas, implementation of management plans for the areas, and expand trans-boundary cooperation on migratory flyway route networks; 11.Request the Parties to support the applications of advanced tools and devices e.g. GPS, radio and satellite transmitters, and remote controllers for identification & monitoring of migratory strategy and provide assistance in analysis of data and findings from database on migratory birds; Mongolia successfully implemented the project to build artificial nests for Saker falcon through its cooperation with the Arabian Emirate. In 2009 and 2010, when drought and dzud (heavy snow fall) occurred, mesh of the border between Russia and Mongolia was taken away for a certain period of time in order to release the Mongolian gazelle migration; Some individuals of migratory birds had radio and satellite image transmitters put on and remote controllers and data on migratory routes and seasons was received. The findings and analysis data are being used for conservation management planning and development of proposals for their conservation; Resolution 10.11. High tension power lines and migratory birds 2.2 Government agencies, scientific institutions, and non-governmental organizations should conduct joint assessment of impacts of power wire lines on bird populations and cooperate with the energy sector in order to discuss policies; 2.3 Identify grounds of distributions, Government agencies, scientific institutions, and non-governmental organizations discuss and cooperate with the energy sector to reduce impacts of power wire lines on bird populations; they provide recommendations e.g. changing designs of power line facilities and 38 herd and population sizes, migration routes, stopover points and breeding sites of migratory birds at regional level and consider the assessment findings for planning of power line construction in order prevent from potential accidents; if such accidents and mortalities are recorded during the studies, it needs to take preventive and remedial actions; 2.5 Identify parts of the power lines that are highly risky for birds or the parts, where injuries and mortalities of birds are found; 3. Call for the Parties, non-member countries, and inter-governmental agencies, and other related parties to reflect the actions recommended by this Decision in their national strategic programmes and action plans for biodiversity conservation and related legislations; Call for the Parties to reflect and discuss the Decision with their national reports and present their findings to respective Parties; Decision 10.28 Saker falcon placing fans on line poles to push away birds based on assessment and monitoring findings; The research institutions and researchers identify the risky parts of power line facilities, where birds might fall in injuries and mortalities, and deliver respective parties the recommendations for changing their designs and taking other necessary preventive and remedial actions; Include Saker falcon populations Supported the proposal to include except for the population in the Saker falcon in the Appendix I Mongolia, in the Appendix I to the to the Convention; Convention on Migratory Species and immediately coordinate cooperation among the Parties; 39 SUCCESS, CONSTRAINTS, & LESSONS LEARNT DURING THE FOLLOW UP ACTIONS OF THE DECISIONS Success & lessons learned: To summarize and conclude the actions implemented and being implemented, the National Council authorized by the Convention on Migratory Species of Wild Animals have been successfully fulfilling its commitments in consistency with international requirements and practices and are constantly taking place in the activities and events organized by the Convention since Mongolia signed the Convention. It is praiseworthy that it has been carrying out many quite reasonable activities when compared to those completed by specific professional institutions and organizations. As a member of the Convention, Mongolia paid its membership fees in a timely manner and has been actively participating at regular meetings of COP and Scientific Council since joining. As seen from the initiatives and comments shared on the meetings of COP, the impressions and feedback of the Convention Secretariat, Mongolia has a high reputation and motivation among other members countries. The Convention Board members were renewed in 2010 and its performances e.g. archiving of previous reports and other related materials have been intensified. Mongolia regularly sent its representatives to the Convention activities and events e.g. Memorandum of Understanding, where Mongolia signed, and related meetings, workshops, and conferences. This active participation in convention activities and events has been very helpful in follow up actions and implementation of the Convention activities and fulfillment of commitments. Governmental and non-governmental organizations of Mongolia have been actively taking place in conservation of the wild species recorded in the Convention Appendices as well being recognized by international communities. It is seen from the proceedings and other materials including reports of the meetings, researches, awareness events, and conservation activities on the species, as well as publications and articles on internationally recognized journals and editions. All these efforts are the cooperative inputs of national researchers, experts, and scientists to the conservation of rare and very rare wild species. Constraints: Management and organizational matters: According to the analysis and assessment findings on national programmes and projects being implemented in the environmental field, the non-compliance or unsatisfactory performances against the expected outputs resulted from inadequate relations and cooperation among respective Ministries and agencies and lack of action plans and performance indicators in most of the programmes as well as indefinite funding sources (National Audit Report, 2010). Awareness and promotions on the Convention and its activities and what importance Mongolia is giving to the Convention, and how Mongolia has been taking place in the Convention activities are missing. A database on the wild species from Mongolia recorded in the Bonn Convention Appendices has not been established yet. It brings about a difficulty in accessing to the data on the wild species and their conservation, research and uses. Decisions of the COP meetings and documents and papers issued from the Convention Scientific Council have been inadequately filed and maintained into file. Access to these materials is limited to the Convention website. A specific feature of the Convention is that conservation and research and monitoring is designed and implemented at the entire habitat level of each species or at 40 regional level. With this regard, Mongolia provided insufficient performances and creativeness to allocate and spend funding. Promotions on the Convention, its goal and objectives, importance and proposed actions are missing at a local level, they are inadequately linked to local development action plans and taking wild species under protection is inadequately managed. Funding is inadequately allocated and spent for conservation and research on some migratory wild species particularly at decision making levels; no specific policy on retaining skilled personal (e.g. managers and officers) at Protected Area administrations; due to a shortage of professional and qualified human resource in local areas, the specialists, officers, and rangers working have inadequate knowledge, skills, education, and experiences; and public awareness activities on the biodiversity importance is insufficiently conducted; When planning in economic and other development sectors, the biodiversity importance, particularly the importance, values, dependence, and biological needs of migratory wild species moving through several provinces’ territories and trans-boundary areas is less considered. Mostly, the issues are addressed after relevant decisions are made. These disadvantages are proven with many examples of wrong planning mechanisms. For instance, mining licenses were issued to 70 per cent of the total country’s territory; when identifying carrying capacities of pastureland, the grassland use by wild animals (herbivores) is not considered, as a result the heads of livestock have been automatically increased and exceeding the pastureland carrying capacities etc. Conservation of migratory wild animals in trans-boundary areas is mostly managed “on paper” through few agreements with the neighboring two countries. However, some physical work e.g. biotechnical measures and actions during unexpected natural disasters e.g. droughts and dzud (heavy snow falls) or during breeding and calving periods, and opening border wire meshes during migrations through transboundary areas are missing and inadequately managed according to the findings of studies and analysis. For migratory birds, a number of individuals are hit on high tension lines and are wounded, injured, and even killed. Thus, it needs to carry out the studies to identify which parts of high tension lines are unprotected or risky for birds and to recommend respective agencies and organizations changing the current design of the electricity lines and their connections in order to make them safer for birds. The Government’s Action Plan for 2008-2012 states: “improve the conservation and preservation of very rare and rare wild species within their natural habitats..., capture and rear some species e.g. Bactrian camel, Saiga, Amur sturgeon within their habitats in order to increase their populations, and use biotechnological benefits for improving their genetic funds”. To implement these objectives, the Ministry of Nature, Environment, and Tourism approved the General Action Plan for Conservation of Very Rare Wild Species by its Resolution No: 329 in 2007. However, the planned actions were too generic, had no specific actions for designated areas, and performances of some actions take time (National Audit Report, 2010). Conservation of migratory wild animals: Border, railway, and other line facilities were designed and built without any crossing areas and gates through which migratory wild animals freely move in and out. Consequently, the migrations, intuitions, and biological and ecological needs of these species are directly held back by these border, railway and other line facilities particularly during their seasonal movements. 41 Among other negative impacts, the intensive development of mining and its associated infrastructure namely railways and auto roads show the most severe impacts on the migratory wild species has provided a basis to reduced habitats and populations. A part “A” of Great Gobi Strictly Protected Area, a main distribution area of Bactrian camel, is inhabited by artisanal or “ninja” miners for their businesses. It provides the most severe pressure to the habitats and distribution areas of the wild species e.g. Bactrian camel, Gobi bear, Khulan, Black–tailed gazelle, and others. As habitats and distribution areas of Snow leopard are occupied and overlapped with grazing of domestic livestock, its prey species e.g. ibex and marmot have run away from their habitats. Thus, attacks by Snow leopard are getting increased and local herders have had revengeful attitude to the species because of their lost livestock. It also causes a reduced population. It is seen illegal & uncontrolled hunting is widely taken as per the reports by local rangers and anti-poaching unit members. Similarly, illegal hunting of other species e.g. Khulan, Black tailed gazelle, and Argali particularly in Umnugovi and Dornogovi provinces is increased and consequently the species’ populations are getting reduced (Institute of Biology, 2009). Continued and increasing illegal hunting of Mongolian saiga would be somehow relevant that the supply of saiga antlers from Kazakhstan to China for traditional medicine has been stopped. It also shows there is a potential latent chain of illegal trade & smuggling of the saiga antlers in the country. Another pressure to the species is overlapping of grazing areas of Saiga and domestic livestock due to drastic increase in livestock heads. Thus, the saiga is disturbed and pushed away from their habitats. Export of the Saker falcon is managed by licenses. However, it is unclear & not disclosed about some issues e.g. how many & what companies and agencies are involved in the licensing, what is the license perspective, how the Saker falcons capture is managed and monitored on the ground, how many individuals of the species have been actually caught in their natural habitats, how many of them were released to the nature, how many have died, what were their reasons, how many individuals have been exported and smuggled through customs, and many other types of relevant information is still missing. There is definitely a lack of information on many issues, but it is not open. All these disadvantages hinder adequate monitoring on Saker falcon population in Mongolia. Considerable amounts of incomes are annually earned from trophy hunting of some species e.g. Saker falcon, Argali, and male Argali and ibex, but the portions of incomes legally stated in legislations are not annually spent for conservation and research on species’ populations and their growth. It leads to impediment to long term sustainable use of the species populations and gradually to their extinction (National Audit Office Report, 2010). 42 ACKNOWLEDGEMENTS We would like to thank to Dr. N. Tseveenmaydag, Head of Ornithological Laboratory of the Institute of Biology, MAS; Dr. S. Gombobaatar, Lecturer of Wildlife Department of School of Biology and Biotechnology, National University of Mongolia; colleagues from Mammalian Ecological Laboratory of the Institute of Biology, MAS; the Snow Leopard Conservation Center; the Wildlife Study and Conservation Center; the WWF Mongolia Programme Office team; the Nature, Environment, and Tourism departments in the provinces, and Protected Area administrations for sharing their reports and reference materials for the report preparation; the Team of International Cooperation Department of MNET for their initiatives to produce the report, and the UNDP Country Office and WWF Mongolia for funding necessary for the report preparation. 43 References Amgalan L. 1984. Distributions and Herd Structures of Black-Tailed Gazelle (Gazella subgutturosa) in Zuungaryn Gobi. A research paper by the Institute of Biology, MAS №19. pages 208-213. Amgalan L. 1986. Distributions and Populations of Black-Tailed Gazelle (Gazella subgutturosa) in Mongolia. A research paper by the Institute of Biology, MAS. №21. 1519. Amgalan L. 1995. Distributions and Population Dynamics of Black-Tailed Gazelle (Gazella subgutturosa) in Mongolia. A report of research conference of “Biology-30th Anniversary”, Institute of Biology, MAS. Ulaanbaatar. Amgalan L. 2000. Ecology and Conservation of Black-Tailed Gazelle in Mongolia. Scientific paper & work for Dr.Sc (in Biology). Ulaanbaatar. Badam Kh. Ariunzul Ya. 2005. (edit.) Compendium of Hunting Laws of Mongolia. Bannikov A.G. 1954. Mammals of the Mongolian People’s Republic. Moscow. (In Russian). Nature and Environment Minister’s Order. 2000. Banning of Hunting of Mongolian Gazelle for Commercial Purpose. Ulaanbaatar. Ministry of Nature and Environment. 1996. “Compendium of Hunting Laws”. Ulaanbaatar. Introduction on the Conventions on Biodiversity Conservation. 2011. A pamphlet. NET, WWF, UNDP Environmental Programme. Ulaanbaatar. National Report on Biodiversity. 4th Edition. 2009. MNET. Ulaanbaatar. Institute of Biology. 1985. Game Species Reserves and a Basis for Sustainable Use in Mongolia. Unpublished Report to the Ministry of Forestry. Ulaanbaatar. Institute of Biology, 2009. Assessment of Steppe and Gobi Ungulate Reserves in Mongolia. Research Report to the MNET. Ulaanbaatar. Institute of Biology. 2010. Assessment of Mountain Ungulate Reserves in Mongolia. A Research Report to the MNET. Ulaanbaatar. Dulamtseren S., Amgalan L. 1995. Current Status of Distributions and Populations of Mongolian Saiga (Saiga tatarica mongolica, Bannikov). (edit. Badamkhand) “Natural and Biological Resource of Great Gobi Strictly Protected Area”. MNE, Ulaanbaatar. pages 45-51. Жирнов Л.В., Гунин П.Д., Адъяа Яд. 2011. “Дикий двугорбый верблюд Центральной Азии: среда обитания, биологические особенности и проблемы 44 сохранения”. Москва. 182 стр. Серия “Биологические ресурсы и природные условия Монголии”, Труды Совместной Российско-Монгольской комплексной биологической экспедиции РАН и АМН. Том 57. Lkhagvasuren B. 2000. Conservation and effects on distribution and populations of Mongolian Gazelle (Procapra gutturosa Pallas, 1777) in Mongolia. PhD Dissertation. Ulaanbaatar. Conservation Status of Very Rare and Rare Wild Species in Mongolia, 2010. National Audit Office Report. Munkhtungalag M, 2011. Interview with the Nature, Environment, and Tourism Minister, L. Gansukh on a national newspaper “Social Mirror”. August 24. Panda newsletter. 2011. Quarterly newsletter published by the WWF Mongolia Programme office (41). Ñîêîëîâ Â.Å., Â.Í. Îðëîâ. 1980. Îïðåäåëèòåëü Ìëåêîïèòàþùèõ Ìîíãîëüñêîé Íàðîäíîé Ðåñïóáëèêè. Èçä-âî “Íàóêà”, Ìîñêâà. A research paper of Hydro-Meteorological Institute. 2009. Ulaanbaatar. Shagdarsuren O. (edit)., Jigj S., Tsendjav D., dulamsuren S., Bold A. munkhbayar Kh., Dulmaa A., Erdenejav G., Ulziikhutag N., Ligaa U., Sanchir Ch. 1987. Mongolian Red Book. MAS publishing house. Shiirevdamba Ts., Shagdarsuren O., Erdenejav G., Amgalan L., Tsetsegmaa Ts. (edit.) 1997. Mongolian Red Book. MNE. ADMON publishing house, Ulaanbaatar. Amgalanbaatar, S., Reading, R.P., Lkhagvasuren, B. and Batsukh, N. (2002b). Argali sheep (Ovis ammon) trophy hunting in Mongolia. Pirineos 157: 129-150. Birdlife International 2001а. Threatened birds of Asia: Bi4rdlife International Red Data Book. Cambridge, UK. Birdlife International. 1516 pp. Birdlife International 2009. The Birdlife checklist of the birds of the world., with conservation status and taxonomic sources. Version 1. Clark, E. L., Munkhbat, J., Dulamtseren, S., Baillie, J. E. M., Batsaikhan, N., Samiya, R. and Stubbe, M. (compilers and editors) (2006). Mongolian Red List of Mammals. Regional Red List Series Vol. 1. Zoological Society of London, London. (In English and Mongolian) Campos-Arceiz, A., Takatsuki, S. and Lkhagvasuren, B. (2004). Food overlap between Mongolian gazelles and livestock in Omnogobi, southern Mongolia. Ecological Research 19: 455-460. CMS website www.cms.int 45 Feh, C., Shah, N., Rowen, M., Reading, R.P. and Goyal, S.P. (2002). Status and action plan for the Asiatic wild ass (Equus hemionus). In: P. Moehlman (ed.) Equids, zebras, asses and horses. IUCN, Gland and Cambridge. pp. 62-70. Gombobaatar, S. and Monks, E.M. (compilers), Seidler, R., Sumiya, D., Tseveenmyadag, N., Bayarkhuu, S., Baillie, J.E.M., Boldbaatar, Sh., Uuganbayar, Ch. (editors) (2011). Regional Red List Series Vol.7. Birds. Zoological Society of London, National University of Mongolia and Mongolian Ornithological Society. (In English and Mongolian). Hare, J. (2006). Counting camels, consulting stones. Geographical Magazine March: 4043. Ito Т, Lkhagvasuren, B., Enkhbileg, D., Takatsuki, S., Tsunekawa, A. Jiang, Z. (2005). Preliminary evidence of a barrier effect of a railroad on the migration of Mongolian gazelles. Conservation Biology 19(3): 945-948. Kaczensky, P., Sheehy, D., Johnson, D., Walzer, C. and Sheehy, C. (2009). Impacts of well rehabilitation and human intrusion on khulan (wild ass) and other threatened species in the Gobi Desert. Final report for the World Bank. Lhagvasuren B., E.J. Milner-Gulland. 1997. The status and management of the Mongolian Gazelle (Procapra gutturosa) population. “Oryx”, Vol.31, No 2. April, 127134. Lkhagvasuren, B., Dulamtseren, S., Amgalan, L., Mallon, D., Schaller, G., Reading, R.P and Mix, H. (1999). Status and conservation of antelopes in Mongolia. Proceedings of the Institute of Biology of the Mongolian Academy of Sciences 1: 96-107. Lhagvasuren B., S. Dulamtseren, L. Amgalan. 2001. Status of Mongolian antelopes. Mallon D.P. and Kingswood S.C. (compilers). Antelopes. Part 4: North Africa, the Middle East, and Asia. Chapter 32: Mongolia. Global Survey and Regional Action Plans. SSC Antelope Specialist Group. IUCN, Gland, Switzerland and Cambridge, UK. Lhagvasuren B. 2007. Population assessment of Khulan (Equus hemionus) in Mongolia. Enforshung biologischer ressourcen der Mongolei. (Halle/Saale) Vol.10., pp. 45-48 Lkhagvasuren B., Chimeddorj B., Sanjmyatav D. 2011. Barriers to migration: analyzing the effects of infrastructure on migratory terrestrial mammals in Mongolia. Case study report to Convention on Migratory Species. Ulaanbaatar. McCarthy, T.M. (2000). Ecology and conservation of snow leopards, Gobi brown bears and wild Bactrian camels in Mongolia. Ph.D. Dissertation, University of Massachusetts, Amherst. 133 pp. McCarthy, T.M. and Chapron, G. (2003). Snow leopard survival strategy. International Snow Leopard Trust and Snow Leopard Network, Seattle. 46 Milner-Gulland E.J., B. Lhagvasuren. Population dynamics of the Mongolian Gazelle Procapra guttuosa: an historical analysis. The Journal of Applied Ecology. 1998. 35, 240-251. Ministry of Nature and Environment (MNE) (1996). Biodiversity conservation action plan for Mongolia. Ministry of Nature and Environment, Ulaanbaatar. (In English and Mongolian) Reading, R.P., Amgalanbaatar, S., Mix, H. and Lkhagvasuren, B. (1997). Argali Ovis ammon surveys in Mongolia’s South Gobi. Oryx 31: 285-294. Reading, R.P., Amgalanbaatar, S., Kenny, D., Onon, Yo., Namshir, Z. and DeNicola, A. (2003). Argali ecology in Ikh Nartiin Chuluu Nature Reserve: Preliminary findings. Mongolian Journal of Biological Sciences 1(2): 3-14. (In English with a Mongolian summary) Reading, R.P., Amgalanbaatar, S., Wingard, G.J., Kenny, D. and DeNicola, A. (2005). Ecology of argali in Ikh Nartiin Chuluu Nature Reserve, Dornogobi Aimag. Erforschung Biologischer Ressourcen der Mongolei (Halle/Saale) (Exploration into the Biological Resources of Mongolia) 9: 77-89. Sokolov, V.E. and Lushchekina, A.A. (1997). Procapra gutturosa. Mammalian Species 571: 1-5. Schaller, G.B. and Lkhagvasuren, B. (1998). A disease outbreak in Mongolian gazelles. Gnusletter 17: 18. Tserenbataa, T. (2003). A genetic study on populations of argali sheep (Ovis ammon) in Mongolia: Implications for conservation. M.Sc. Thesis, Department of Biology, University of Denver, Denver. Tserenbataa, T., Ramey II, R.R., Ryder, O.A., Quinn, T.W. and Reading, R.P. (2004). A genetic comparison of populations of argali sheep (Ovis ammon) in Mongolia using the ND5 gene of mtDNA: Implications for conservation. Molecular Ecology 13: 1333-1339. Walzer, C. and Kaczensky, P. (2005). Wild camel training and collaring mission for the Great Gobi A Strictly Protected Area in Mongolia. Report to the United Nations Development Programme (UNDP), Ulaanbaatar. Wingard, G. (2005). Seasonal food habits of argali and dietary overlap with domestic livestock in Mongolia. M.Sc. Thesis, University of Montana, Missoula. Wingard J.R. and Zahler, P. (2006). Silent Steppe: The Illegal Wildlife Trade Crisis in Mongolia. Mongolia Discussion Papers, East Asia and Pacific Environment and Social Development Department. Washington D.C.: World Bank. WWF Mongolia Programme Office, 2010. Saiga conservation project report to MAVA foundation. 47 Zahler, P., Lkhagvasuren, B., Reading, R.P., Wingard, G.J., Amgalanbaatar, S., Gombobaatar, S., Barton, N. and Onon, Yo. (2004). Illegal and unsustainable wildlife hunting and trade in Mongolia. Mongolian Journal of Biological Sciences 2(1): 23-31. (In English with a Mongolian summary) 48 Annex 1 List of species included from Mongolia in Appendix I and II of the Bonn convention № Анги/Class Баг/Order Овог/Family Зүйл/Specie Аль s популяци/P opulations Хэзээ оруул сан/W hen added Appendix I Хуурай газрын хөхтөн/Terrestrial mammals 1 2 Mammalia Carnivora Artiodactyla Felidae Camelidae Uncia uncia Camelus bactrianus Formerly listed Panthera uncia All COP I as COP 7 Шувуу/Birds Dalmatian Pelican Oriental Stork Lesser Whitefronted Goose Swan Goose Baikal Teal Ferruginous Pochard Baer's Pochard White-headed Duck Greater Spotted Eagle Imperial Eagle Pallas's SeaEagle White-tailed Eagle Egyptian Vulture Lesser Kestrel Red-Crowned Crane Siberian Crane White-naped Crane Hooded 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 49 COP-1 COP-5 COP-7 COP-7 COP-5 COP-9 COP-4 COP-5 COP-5 COP-7 COP-1 COP-9 COP-5 COP-7 COP-7 Crane Sociable Lapwing Relict Gull Yellowbreasted Bunting Saker falcon 19 20 21 22 COP-5 COP-9 COP-10 Мөлхөгчид/Reptilia 1 Загас/Pisces 1 Appendix II Хуурай газрын хөхтөн/Terrestrial mammals 1 Mammalia 2 Perissodactyla Equidae Artiodactyla Bovidae 3 4 5 Equus hemionus Gazella subgutturos a Procapra gutturosa Saiga borealis mongolica All COP 7 All COP 7 All COP 7 Ovis ammon All COP 10 all COP 6 all COP 6 All Шувуу/Birds (тусад нь жагсаалт гаргасан болно) Мөлхөгчид/Reptilia 1 Actinopterygii Acipenseriformes Загас/Pisces Acipenseridae 50 Acipenser baerii baicalensis Acipenser schrenckii Монгол нэр/Current names Àíãëè нэр/English names 0 1 2 3 GAVIIFORMES Gaviidae Gavia Gavia arctica PODICIPEDIFORMES Podicipididae Podiceps Podiceps grisegena PELECANIFORMES Pelecanidae Pelecanus ÀÕÓÓÍÒÀÍÛ ÁÀà Àõóóíûõàíû îâîã Àõóóíà Õèëýí îìðóóò àõóóíà ØÓÍÃÓÓÐÒÀÍÛ ÁÀà Øóíãóóðûíõàíû îâîã Øóíãóóð Áóóðàë øóíãóóð ÕÎÒÎÍÒÎÍÛ ÁÀà Õîòîíãèéíõîíû îâîã Õîòîí ÃÀÕÓÓÍÒÀÍ Ãàõóóíûõàí Ãàõóóí Õèëýíã¿åý ãàõóóí ØÓÍÃÓÓÐÒÀÍ Øóíãóóðûíõàí Øóíãóóð Áóóðàë øóíãóóð ÕÎÒÎÍÒÎÍ Õîòîíãèéíõîí Õîòîí Pelecanus crispus CICONIIFORMES Threskiornithidae Platalea Áîðöãîð õîòîí ªÐÂÈÒªÍÈÉ ÁÀà Áèë¿¿ñèéíõýíèé îâîã Áîðöãîð õîòîí ªÐÂÈÉÒªÍ Áèë¿¿ñèéíõýí Õàëáàãàíò 51 CMS-II хавсралт Õóó÷èí íýð/Old Mongolian names CMS-I хавсралт Латин нэр/Latin name Монгол орны шувууны орших хэлбэр 2007 оны 1-р сарын байдлаар/type of occurence Монгол орны шувуу (Болд,Болдбаатар нар, 2002) LIST OF BIRD SPECIES INCLUDED IN CMS APPENIX I AND II AND TYPE OF THEIR OCCURENCE Black -throated Loon НӨ НӨ COP-4 Red-necked Grebe НӨ ДӨ COP-4 НӨ НӨ Dalmatian Pelican COP1 COP-4 4 Õàëáàãàí õóøóóò ªðâèéõºíèé îâîã 8 9 Platalea leucorodia Ciconiidae Ciconia Ciconia boyciana Ciconia nigra PHOENICOPTERIFORMES Phoenicopteridae Phoenicopterus Phoenicopterus roseus ANSERIFORMES Anatidae Anser Anser anser Anser fabalis Íàë äýãëèé ÃÀËÓÓÒÀÍÛ ÁÀà Íóãàñíûõàíû îâîã Ãàëóó Áîð ãàëóó Áóóðàë ãàëóó Öàãààí õàëáàãàíò ªðâèéíõºí ªðºâòàñ Äîðíûí ºðºâòàñ Õàð ºðºâòàñ ÍÀËÒÀÍ Íàëûíõàí Íàë ßãààí íàë ÃÀËÓÓÒÀÍ Íóãàñíûõàí Ãàëóó Áîð ãàëóó Áóóðàë ãàëóó 10 Anser albifrons Ìàíõèí ãàëóó Ìàíõèí ãàëóó 5 6 7 11 12 13 14 15 16 17 18 19 20 Anser erythropus Anser indica Anser cygnoides Cygnus Cygnus cygnus Cygnus olor Cygnus bewickii Dendrocygna Dendrocygna javanica Tadorna Tadorna ferruginea Tadorna tadorna Anas Anas platyrhynchos Õàð õóøóóò ºðºâòàñ Õàð ºðºâòàñ Íàë äýãëèéíõýíèé îâîã Îäîé ãàëóó Õýýðèéí ãàëóó Õîøóó ãàëóó Õóí Ãàíãàð õóí Õóðóóò õóí Ãóíãàð õóí Àíãèð Àíãèð Àíõèäàë Íóãàñ çýðëýã íóãàñ 52 Îäîé ãàëóó Õýýðèéí ãàëóó Õîøóó ãàëóó Õóí Ãàíãàð õóí Õóðóóò õóí Ãóíãàð õóí Àíõèð Ìîäíû àíõèð Àíãèð Õîíäîí àíãèð Àíõèäàë àíãèð Íóãàñ Çýðëýã íóãàñ Eurasian Spoonbill НӨ НӨ Oriental Stork Black Stork Т НӨ Т НӨ Т Т + НӨ ДӨ НӨ ДӨ + + ДӨ ДӨ Greater Flamingo Greylag Goose Bean Goose Greater White-fronted Goose Lesser White-fronted Goose Bar-headed Goose ДӨ ДӨ НӨ НӨ + + + + COP5 + COP7 НӨ НӨ НӨ НӨ ДӨ НӨ НӨ ДӨ + + + Т Т + Ruddy Shelduck Common Shelduck НӨ НӨ НӨ НӨ + + Mallard НӨ НӨ + Swan Goose Whooper Swan Mute Swan Bewick's Swan Lesser Whistling-Duck НӨ НӨ НӨ НӨ ДӨ ДӨ НӨ НӨ НӨ НӨ НӨ НӨ НӨ НӨ НӨ НӨ НӨ НӨ + + + + + + Т Т + Red -crested Pochard НӨ НӨ + Common Pochard НӨ НӨ 21 22 Anas poecilorhynchos Anas crecca çýðëýãøèð íóãàñ Íîãîîõîí íóãàñ Çýðëýãøèð íóãàñ Íîãîîõîí íóãàñ Spot-billed Duck Common Teal 23 24 25 26 27 28 29 Anas formosa Anas falcata Anas strepera Anas penelope Anas acuta Anas guerguedula Anas clypeata Aix Aix galericulata Netta Netta rufina Aythya Aythya ferina Áàéãàëèéí íóãàñ Ãýçýãò íóãàñ Áîð íóãàñ Çýýðä àëàã íóãàñ Øîâòãîð àëàã íóãàñ Öàãààí õºìñºãò íóãàñ Õàëáàãà íóãàñ Áàéãàëèéí íóãàñ Ãýçýãò íóãàñ Áîð íóãàñ Çýýðä íóãàñ Øîâòãîðàëàã íóãàñ Öàãààíõºìñºãò íóãàñ Õàëáàãà íóãàñ Óðàíõàæèí Ìàíäèð óðàíõàæèí Áèâààí Óëààíõóøóó áèâààí Øóìáóóð Óëààíõ¿ç¿¿ øóìáóóð Baikal Teal Falcated Duck Gadwall Eurasian Wigeon Northern Pintail Garganey Northern Shoveler 30 31 32 Õàëçàí àíãèð Óëààí õóøóóò øóìáóóð Øóìáóóð Óëààí õ¿ç¿¿ò øóìáóóð Mandarin Duck ДӨ ДӨ НӨ НӨ НӨ Т + + Harlequin Duck Т Т Long-tailed Duck Т + + + Óíäàð í¿äýí øóìáóóð Óíäàð øóìáóóð Ferruginous Pochard 34 35 36 Aythya baeri Aythya fuligula Aythya marila Histrionicus Histrionicus histrionicus Clangula Clangula hyemalis Bucephala Bucephala clangula Melanitta Melanitta deglandi Oxyura Óõàà øóìáóóð Ãýçýãò øóìáóóð Òýíãèñèéí øóìáóóð Óõàà øóìáóóð Ãýçýãò øóìáóóð Òýíãèñèéí øóìáóóð ׺ðõ Õîòãóóæèí ÷ºðõ Øóíãààõàé ̺íãºëºã øóíãààõàé Øóíãàà÷ Àëàã øóíãàà÷ Ìîíõäîé Òîëüò ìîíõäîé ßìààíñ¿¿ëò Baer's Pochard Tufted Pochard Greater Scaup Oxyura leucocephala ßìààí ñ¿¿ëò Öàãààíòîëãîé ÿìààíñ¿¿ëò White-headed Duck 38 39 40 41 Àëàã øóíãàà÷ ĺðò íóãàñ 53 + COP5 COP9 НӨ Aythya nyroca Õîòãóóæèí íóãàñ COP7 НӨ 33 37 + + Common Goldeneye НӨ НӨ + White-winged Scoter НӨ НӨ + НӨ НӨ COP4 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60 61 62 Mergus Mergus albellus Mergus serrator Mergus merganser FALCONIFORMES Pandionidae Pandion Pandion haliaetus Accipitridae Pernis Pernis apivorus Pernis ptilorhyncus Milvus Milvus migrans Circus Circus cyaneus Circus macrourus Circus pygargus Circus melanoleucus Circus aeruginosus Circus spilonotus Accipiter Accipiter gentilis Accipiter nisus Accipiter badius Accipiter gularis Buteo Buteo lagopus Buteo hemilasius Buteo rufinus Buteo buteo Butastur Öàõèóð íóãàñ Ñýâãýð íóãàñ Õóìõèí íóãàñ ÌÀÕ×ÈÍ ØÓÂÓÓÄÒÀÍÛ ÁÀà ßâëàãûõàíû îâîã ßâëàã ñàð Õàðöãàéíõàíû îâîã Ãîîðáèñ Ñîãñîîò çºãèé÷ ñàð Ñîõîð ýëýý Ñàõèà Öàãààí ýëýãò Õýýðèéí öàãààí ýëýãò Íóãûí öàãààí ýëýãò Ñààðàë öàãààí ýëýãò Íàìãèéí öàãààí ýëýãò Õàðöãàé ¯ëýã õàðöãàé Ìîðèí õàðöãàé ¯¿ðñýý õàðöãàé Øóíãàà÷ õàðöãàé Ñàð Òàðëàí ñàð Øèëèéí ñàð Òàëûí ñàð Ñàð 54 Áîõèî Öàõèóð áîõèî Ñýâãýð áîõèî Õóìõèí áîõèî ØÎÍÕÎÐÒÎÍ ßâëàãèéíõàí ßâëàã Çàãàñ÷ ÿâëàã Õàðöàãûíõàí Ãîîðáèñ Áàë÷ ãîîðáèñ Ñîãñîîò ãîîðáèñ Ýëýý Ñîõîð ýëýý Õóëä Ñààðàë õóëä Õýýðèéí õóëä Íóãûí õóëä Àëàã õóëä Íàìãèéí õóëä Äîðíûí õóëä Õàðöàãà ¯ëýã õàðöàãà Ìîðèí õàðöàãà ¯¿ðñýý õàðöàãà Øóíãàà÷ õàðöàãà Ñàð Òàðëàí ñàð Øèëèéí ñàð Òàëûí ñàð Îéí ñàð Õàðöãàé Smew Red -breasted Merganser Common Merganser ДӨ ДӨ НӨ ДӨ ДӨ НӨ + + + Osprey НӨ НӨ + European Honey-Buzzard Oriental Honey-Buzzard ДӨ НӨ ДӨ НӨ + + Black Kite НӨ НӨ + Northern Harrier Pallid Harrier Montagu 's Harrier Pied Harrier Western Marsh Harrier Eastern Marsh-Herrier НӨ ДӨ НӨ НӨ НӨ НӨ НӨ ДӨ НӨ НӨ НӨ + + + + + + Northern Goshawk Eurasian Sparrowhawk Shikra Japanese Sparrow Hawk НӨ НӨ Т НӨ НӨ НӨ Т НӨ + + + + Rough-legged Buzzard Upland Buzzard Long -legged Buzzard Common Buzzard ӨИ С ДӨ НӨ НӨ НӨ ДӨ ӨИ + + + + 63 64 65 66 67 68 Butastur indicus Circaetus Circaetus gallicus Spizaetus Spizaetus nipalensis Hieraaetus Hieraaetus pennatus Hieraaetus fasciatus Aquila Aquila nipalensis Ëóñ÷ ñàð Áàõèì á¿ðãýä Õàðñóí á¿ðãýä Á¿ðãýä Òàðâàæè á¿ðãýä Ñàðæóó õàðöãàé Çàãàëàé Ìîãîé÷ çàãàëàé Ñîãñîîòá¿ðãýä Óóëûí ñîãñîîòá¿ðãýä Á¿ðãýäýé Áàõèì á¿ðãýäýé Õàðñóí á¿ðãýäýé Á¿ðãýä Òàðâàæè á¿ðãýä Grey-faced Buzzard НӨ НӨ + Mountian Hawk-Eagle Т Т + Booted Eagle Bonelli's Eagle НӨ Т НӨ Т + + Steppe Eagle НӨ НӨ НӨ НӨ НӨ С С НӨ З НӨ НӨ С С Т Т Cinereous Vulture С С + Eurasian Griffon Himalayan Griffon Т НӨ Т Т + + Gyrfalcon ӨИ ӨИ + Áîð á¿ðãýä Áîð á¿ðãýä Greater Spotted Eagle 70 71 Aquila heliaca Aquila chrysaetos Haliaeetus Õàí á¿ðãýä Öàðìûí á¿ðãýä ͺìðºã Õàí á¿ðãýä Öàðìûí á¿ðãýä ͺìðºãá¿ðãýä Imperial Eagle Golden Eagle 72 Haliaeetus leucoryphus Óñíû íºìðºã á¿ðãýä Óñíû íºìðºãá¿ðãýä Pallas's Sea-Eagle 73 Haliaeetus albicilla Gypaetus Gypaetus barbatus Neophron Óñíû öàãààí ñ¿¿ëò á¿ðãýä Öàãààíñ¿¿ë íºìðºãá¿ðãýä ¨ë Îî÷ ¸ë ¨ëîí White-tailed Eagle Neophron percnopterus Aegypius Aegypius monachus Gyps Gyps fulvus Gyps himalayensis Falconidae Falco Falco rusticolus Äýëò á¿ðãýä Òàñ Íîõîé òàñ Õàæèð Óõàà õàæèð á¿ðãýä Öàñòíû õàæèð á¿ðãýä Øîíõîðûíõîíû îâîã Øîíõîð Æàäàí øîíõîð Äýëò ¸ëîí Òàñ ͺìðºã òàñ Õàæèð Óõàà õàæèð Õèìàëàéí õàæèð Øîíõîðûíõîí Øîíõîð Öàãààí øîíõîð Egyptai Vulture 75 76 77 78 79 55 + COP5 COP5 НӨ Aquila clanga ¨ë + Short-toed Snake-Eagle 69 74 Т Lammergeier + COP7 COP1 + COP9 НӨ НӨ Т НӨ НӨ НӨ НӨ НӨ НӨ Т НӨ НӨ НӨ НӨ НӨ НӨ НӨ НӨ + Common Quail НӨ НӨ + Red-Crowned Crane Siberian Crane Common Crane Т ДӨ НӨ Т ДӨ НӨ + + НӨ НӨ ДӨ ДӨ COP7 COP7 Demoiselle Crane НӨ НӨ + Corn Crake НӨ НӨ + Great Bustard НӨ НӨ COP-1 80 81 82 83 84 85 86 Falco cherrug Falco pelegrinoides Falco peregrinus Falco subbuteo Falco columbarius Falco vespertinus Falco amurensis Èäëýã øîíõîð Øèëèéí øîíõîð Ýãýë øîíõîð Øóóìàí øîíõîð Õàéðãóóíà øîíõîð Òóðàìòàé øîíõîð Àìàðûí òóðàìòàé øîíõîð Èäëýã øîíõîð Øèëèéí øîíõîð Ýãýë øîíõîð Øóóìàí øîíõîð Õàéðãóóíà øîíõîð Òóðàìòàé øîíõîð Àìàðûí øîíõîð Saker Falcon Barbary Falcon Peregrine Falcon Eurasian Hobby Merlin Red-footed Falcon Amur Falcon 87 88 Çýýðä øîíõîð Íà÷èí øîíõîð ÒÀÕÈÀÒÀÍÛ ÁÀà Ãóðãóóëèéíõàíû îâîã Á¿äíýý Á¿äíýý ÒÎÃÎÐÓÓÒÀÍÛ ÁÀà Òîãîðóóíûõàíû îâîã Òîãîðóó Àëàã òîãîðóó Öàãààí òîãîðóó Õàðõèðàà òîãîðóó Çýýðä øîíõîð Íà÷èí øîíõîð ÒÀÕÈÀÒÀÍ Ãóðãóóëûíõàí Áºäíº Ýãýë áºäíº ÒÎÃÎÐÓÓÒÀÍ Òîãîðóóíûõàí Òîãîðóó Àëàã òîãîðóó Öàãààí òîãîðóó Õàðõèðàà òîãîðóó Lesser Kestrel Common Kestrel 90 91 92 Falco naumanni Falco tinnunculus GALLIFORMES Phasianidae Coturnix Coturnix coturnix GRUIFORMES Gruidae Grus Grus japonensis Grus leucogeranus Grus grus 93 Grus vipio Öýí òîãîðóó Öýí òîãîðóó White-naped Crane 94 Grus monacha Anthropoides Anthropoides virgo Rallidae Crex Crex crex Otididae Otis Otis tarda Õàð òîãîðóó Õàð òîãîðóó Òîãèðóó ªâºãò òîãèðóó Ò¿íæ¿¿ðèéíõýí Ò¿íæèí ßâãàí ò¿íæèí Òîîäîãèéíõîí Òîîäîã Õîíèí òîîäîã Hooded Crane 89 95 96 97 ªâºãò òîãîðóó Ò¿íæ¿¿ðèéíõýíèé îâîã Òàðèàí ò¿íæ¿¿ð Òîîäãèéíõîíû îâîã Òîîäîã Òîîäîã 56 + + + + + + + COP5 + 98 99 100 101 102 103 104 105 106 107 108 109 110 111 112 113 Chlamydotis Chlamydotis undulata CHARADRIIFORMES Rostratulidae Rostratula Rostratula benghalensis Charadriidae Pluvialis Pluvialis squatarola Pluvialis fulva Charadrius Charadrius hiaticula Charadrius dubius Charadrius leschenaultii Charadrius mongolus Charadrius veredus Charadrius alexandrinus Eudromias Eudromias morinellus Chettusia Chettusia gregaria Vanellus Vanellus vanellus Microsarcops Microsarcops cinereus Arenaria Arenaria interpres Recurvirostridae Himantopus Himantopus himantopus Recurvirostra Æîðîî òîîäîã ÕªÃׯ¯ÒÍÛ ÁÀà ªíãºò õàðààëæèéíõàíû îâîã ªíãºò õàðààëæ Õèàçèéíõàíû îâîã Ñ¿âýý öàãààí Áóóðàë ñ¿âýý öàãààí Àçèéí ñ¿âýý öàãààí Õèàçàò Õ¿ç¿¿â÷èò õèàçàò Íàðèéí õèàçàò Çýâýí õèàçàò Ìîíãîë õèàçàò Äîðíîäûí õèàçàò Òýíãèñèéí õèàçàò Óðèàíõàéí ñ¿âýý öàãààí Õàâòãààëæ Õàâòãààëæ Ñààðàë õàâòãààëæ ªíäãºí àëàã Ýýòýíãèéíõýíèé îâîã Õèëýí æèã¿¿ðò 57 Òîîäãîé Æîðîî òîîäãîé ÕÈÀÇÒÀÍ Õàðààëæèðûíõàí Õàðààëæèð ªíãºò õàðààëæèð Õèàçàòûíõàí Ñ¿âýýöàãààí Áóóðàë ñ¿âýýöàãààí Àçèéí ñ¿âýýöàãààí Õèàçàò Õ¿ç¿¿â÷èò õèàçàò Íàðèéí õèàçàò Çýâýí õèàçàò Ìîíãîë õèàçàò Äîðíûí õèàçàò Òýíãèñèéí õèàçàò Öàãààíõèàçàò Óðèàíõàéí öàãààíõèàçàò Õàâòãàëæ Õýýðèéí õàâòãàëæ Õàâòãààëæ Óìàðäûí õàâòãààëæ Çóóíõóðãà Ñààðàë çóóíõóðãà Õàéðãà÷ Àëàã õàéðãà÷ Ýýòýíãèéíõýí Õèëýíæèã¿¿ð Ýãýë õèëýíæèã¿¿ð Ýýòýí НӨ НӨ + Greater Painted Snipe Т Т + Grey Plover Pacific Golden-Plover ДӨ ДӨ ДӨ ДӨ + + Common Ringed Plover Little Ringed Plover Greater Sand plover Mongolian Plover Oriental Plover Kentish Plover ДӨ НӨ НӨ НӨ? НӨ НӨ ДӨ НӨ НӨ НӨ? НӨ НӨ + + + + + + Eurasian Dotterel НӨ НӨ + Т Т Northern Lapwing НӨ НӨ + Grey-headet Lapwing ДӨ ДӨ + Ruddy Turnstone ДӨ ДӨ + Black-winged Stilt НӨ НӨ + Houbara Bustard Sociable Lapwing COP5 + 114 115 116 117 118 119 120 121 122 123 124 125 126 127 128 129 130 131 132 133 134 135 136 Recurvirostra avosetta Scolopacidae Tringa Tringa ochropus Tringa glareola Tringa nebularia Tringa totanus Tringa erythropus Tringa stagnatilis Heteroscelus Heteroscelus brevipes Heteroscelus incana Actitis Actitis hypoleucos Xenus Xenus cinereus Phalaropus Phalaropus lobatus Phalaropus fulicarius Phylomachus Phylomachus pugnax Calidris Calidris minuta Calidris ruficollis Calidris subminuta Calidris temminckii Calidris ferruginea Calidris alpina Calidris acuminata Calidris alba Calidris canutus Limicola Ýýòýí Õàðààëæèéíõàíû îâîã Õºã÷¿¿ Ñ¿¿ë öàãààí õºã÷¿¿ Øóãóéí õºã÷¿¿ ¯õýð õºã÷¿¿ Óëààí õºëò õºã÷¿¿ Õàð õºã÷¿¿ Á¿ðäíèé õºã÷¿¿ Áóóðàë õºã÷¿¿ Öýëäýí õºã÷¿¿ Õàéðãûí õºã÷¿¿ Ìàòèãàð õºã÷¿¿ Íàðèéí ñýëýýõýé Íîîëîëäîé Ýëñýã Îäîé ýëñýã Øàð ò¿ð¿¿ò ýëñýã Ñàâàð ýëñýã Òåììèíñêèéí ýëñýã Õàäóóð ýëñýã Õàð ýëñýã Ñ¿¿ë ýëñýã Ãóðâàëæ ýëñýã Øàðìàã ýëñýã 58 Àëàã ýýòýí Õîìíîîòûíõîí Õºã÷¿¿ Ñ¿¿ëöàãààí õºã÷¿¿ Øóãóéí õºã÷¿¿ ¯õýð õºã÷¿¿ Óëààíõºëò õºã÷¿¿ Õàð õºã÷¿¿ Á¿ðäíèé õºã÷¿¿ Õºã÷¿¿õýé Áóóðàë õºã÷¿¿õýé Öýëäýí õºã÷¿¿õýé Õàéðãûíõºã÷¿¿ Ýãýë õàéðãûíõºã÷¿¿ Õºã÷¿¿ëýã Ìàòèãàð õºã÷¿¿ëýã Ñýëýýõýé Íàðèéí ñýëýýõýé Улаан сэлээхэй Íîîëîëäîé Íîöîî íîîëîëäîé Ýëñýã Îäîé ýëñýã Øàðò¿ð¿¿ò ýëñýã Ñàâàð ýëñýã Òåììèíñêèéí ýëñýã Õàäóóð ýëñýã Õàð ýëñýã Ñ¿¿ë ýëñýã Ãóðâàëæ ýëñýã Øàðìàã ýëñýã Øàë÷èã Pied Avocet НӨ НӨ + Green Sandpiper Wood Sandpiper Common Greenshank Common Redshank Spotted Redshank Marsh Sandpiper НӨ НӨ НӨ? НӨ З НӨ НӨ НӨ ДӨ НӨ З НӨ + + + + + + Asian Wandering Tattler Wandering Tattler ДӨ Т ДӨ Т + + Common Sandpiper НӨ НӨ + Terek Sandpiper НӨ? ДӨ + З Т З + + Ruff ДӨ ДӨ + Little Stint Rufous-necked Stint Long-toed Stint Temminck's Stint Curlew Sandpiper Dunlin Sharp-tailed Sandpiper Sanderling Red Knot ДӨ ДӨ ДӨ З З ДӨ З ДӨ Т ДӨ ДӨ ДӨ З З ДӨ З ДӨ Т + + + + + + + + + Red-necked Phalarope Red Phalarope 137 138 139 140 141 142 143 144 145 146 147 148 149 150 151 152 153 154 155 Limicola falcinellus Lymnocryptes Lymnocryptes minimus Gallinago Gallinago gallinago Gallinago megala Gallinago stenura Gallinago solitaria Scolopax Scolopax rusticola Numenius Numenius minutus Numenius arquata Numenius madagascariensis Numenius phaeopus Limosa Limosa limosa Limosa lapponica Limnodromus Limnodromus scolopaceus Limnodromus semipalmatus Laridae Larus Larus relictus Larus genei Chilidonias Chlidonias niger Sterna Sterna albifrons COLUMBIFORMES Columbidae Ñÿìáè ýëñýã Õºã÷¿¿õýé Õàðààëæ غâãºí õàðààëæ Øóãóéí õàðààëæ Çàìáûí õàðààëæ ªí÷èí õàðààëæ Õîìíîîò Òóòãàëæèí Áè÷èëõýí òóòãàëæèí Ìîðèí òóòãàëæèí Ìàäàãàñêàð òóòãàëæèí Áýñðýã òóòãàëæèí Öóóöàëü Ìîðèí öóóöàëü Õóðãàí öóóöàëü Õàðààëæèí öóóöàëü Àçèéí öóóöàëü Öàõëàéíõàíû îâîã öàõëàé Ðåëèêò öàõëàé غâãºð öàõëàé Õèëýí õàðààëàé Õóðãàí õàðààëàé ÒÀÃÒÀÀÒÍÛ ÁÀà Òàãòààíûõàíû îâîã 59 Ñÿìáè øàë÷èã Ñàëàëæ Áè÷èë ñàëàëæ Õàðààëæ غâãºí õàðààëæ Øóãóéí õàðààëæ Çàìáûí õàðààëæ ªí÷èí õàðààëæ Õîìíîîò Áóóðàë õîìíîîò Òóòãàëæèí Áè÷èëõýí òóòãàëæèí Ìîðèí òóòãàëæèí Ìàäàãàñêàð òóòãàëæèí Áýñðýã òóòãàëæèí Öóóöàë Ìîðèí öóóöàë Õóðãàí öóóöàë Öóóöèë Õàðààëæèí öóóöèë Àçèéí öóóöèë Öàõëàéíõàí Öàõëàé Ðåëèêò öàõëàé غâãºð öàõëàé Õàðààëçàé Õèëýí õàðààëçàé Õàðààëàé Õóðãàí õàðààëàé ÒÀÃÒÀÀÒÀÍ Òàãòààíûõàí Broad-billed Sandpiper ДӨ ДӨ + Jack Snipe ДӨ ДӨ + Common Snipe Swinhoe's Snipe Pintail Snipe Solitary Snipe НӨ НӨ НӨ НӨ НӨ НӨ НӨ НӨ + + + + Eurasian Woodcock НӨ НӨ + Little Curlew Eurasian Curlew Far Eastern Curlew Whimbrel ДӨ НӨ З ДӨ ДӨ НӨ З ДӨ + + + + Black-tailed Godwit Bar-tailed Godwit НӨ З З + + Long-billed Dowitcher Asian Dowitcher Т НӨ Т НӨ + + Relict Gull Slender-billed Gull НӨ Т НӨ Т Black Tern НӨ НӨ COP-4 Little Tern НӨ НӨ COP-4 + + 156 157 158 159 160 161 162 163 164 165 166 167 168 169 170 171 172 173 174 Streptopelia Streptopelia turtur PASSERIFORMES Õ¿¿ðçãýíý Õ¿¿ðçãýíý ÁÎÐ ØÓÂÓÓÒÀÍÛ ÁÀà տ¿ðçãýíý ªðíèéí õ¿¿ðçãýíý ÁÎÐØÓÂÓÓÒÀÍ Muscicapidae Ficedula Íàìíààõàéíûõàíû îâîã Íàìíààõàé Íàìíààõàéíõàí Íàìíàà Ficedula zanthopygia Ficedula narsissina Ficedula mugimaki Ficedula parva Muscicapa Muscicapa striata Muscicapa sibirica Muscicapa latirostris Muscicapa griseisticta Saxicola Saxicola torquata Saxicola insignis Oenanthe Oenanthe oenanthe Oenanthe pleschanka Oenanthe isabellina Oenanthe deserti Monticola Ãóóëèí õîíäëîé íàìíààõàé Ãóóëèí íàìíàà Íàðàí íàìíàà Òàéãûí íàìíàà Õóðãàí íàìíàà Íàìíààõàé Áºðòºò íàìíààõàé Øèâýð íàìíààõàé Äàãóóðûí íàìíààõàé Ñýâõýò íàìíààõàé Øóëãàíàà Ýãýë øóëãàíàà ªãººëýé øóëãàíàà ×îã÷èãî Àäóó÷ ÷îã÷èãî Ìÿðààí ÷îã÷èãî Á¿æèì÷ ÷îã÷èãî Öºëèéí ÷îã÷èãî Æèæèð Monticola saxatilis Monticola solitarius Petrophila Petrophila gularis Phoenicurus Phoenicurus phoenicurus Öîõèîíû õººíäýé Öàðìûí õººíäýé Òàéãûí íàìíààõàé Õóðãàí íàìíààõàé Áºðòºò íàìíààõàé Øèâýð íàìíààõàé Äàãóóðûí íàìíààõàé Ñýâõýò íàìíààõàé Øóëãàíàà Õàð ýðõýò øóëãàíàà ªãººëýé øóëãàíàà ×îã÷îîõîé Àäóó÷ ÷îã÷îîõîé Ìÿðààí ÷îã÷îîõîé Á¿æèì÷ ÷îã÷îîõîé Öºëèéí ÷îã÷îîõîé Öàãààí ã¿åýò õººíäýé Ãàë ñ¿¿ëò Ãàë ñ¿¿ëò 60 Õàäíû æèæèð Öýíõýð æèæèð Äîíãîð Öàãààíã¿åý äîíãîð Ãàëñ¿¿ëò Ýãýë ãàëñ¿¿ëò Eurasian Turtle-Dove НӨ НӨ COP-7 Miscicapidae M.(s.l.) spp Yellow-rumped Flycatcher Narcissus Flycatcher Mugimaki Flycatcher Red-breasted Flycatcher НӨ НӨ НӨ НӨ НӨ НӨ НӨ + + + + Spotted Flycatcher Dark-sided Flycatcher Asian Brown Flycatcher Grey-streaked Flycatcher НӨ НӨ НӨ Т НӨ НӨ НӨ Т + + + + Common Stonechat White-throated Bushchat НӨ НӨ НӨ НӨ + + Northern Wheatear Pied Wheatear Isabelline Wheatear Desert Wheatear НӨ НӨ НӨ НӨ НӨ НӨ НӨ НӨ + + + + Rufous-tailed RockThrush Blue Rock-Thrush НӨ НӨ НӨ НӨ + + Guyanan Solitaire НӨ НӨ + Common Redstart НӨ НӨ + 175 176 177 178 179 180 181 182 183 184 185 186 187 188 189 190 191 192 193 194 195 196 197 198 Phoenicurus ochruros Phoenicurus erythronotus Phoenicurus auroreus Phoenicurus erythrogaster Luscinia Luscinia megarhynchos Luscinia calliope Luscinia svecica Luscinia cyana Luscinia sibilans Tarsiger Ìîéëîí ãàë ñ¿¿ëò Óëáàð ãàë ñ¿¿ëò Õºõ çàðëàãàò ãàë ñ¿¿ëò Öýýæìýãò ãàë ñ¿¿ëò Ãóðãàëäàé Çóëáàðàí ãóðãàëäàé Õóíäàí ºíãºë¿¿ðò ãóðãàëäàé Ñîíäîðò ãóðãàëäàé Íîìèí çàí÷èò ãóðãàëäàé Øèéãíýý ãóðãàëäàé Ìîéëîí ãàëñ¿¿ëò Óëáàð ãàëñ¿¿ëò Äàãóóð ãàëñ¿¿ëò Öýýæìýã ãàëñ¿¿ëò Ãóðãàëäàé Çóëáàðàí ãóðãàëäàé ªíãºë¿¿ðò ãóðãàëäàé Ñîíäîðò ãóðãàëäàé Íîìèí ãóðãàëäàé Øèéãíýý ãóðãàëäàé Õºõçîîò Tarsiger cyanurus Turdus Turdus obscurus Turdus pallidus Turdus ruficollis Turdus atrogularis Turdus naumanni Turdus eunomus Turdus pilaris Turdus viscivorus Turdus iliacus Turdus philomelos Turdus merula Turdus sibiricus Zoothera Zoothera dauma Emberizidae Emberiza Õºõ çîîò Õººíäýé Õàëèóí õººíäýé Á¿ãýýí õººíäýé Óëààí ã¿åýò õººíäýé Õàð ã¿åýò õººíäýé Íàóìàííû õººíäýé Õ¿ðýí õººíäýé Äóóëãàò õººíäýé Áóæìàã õººíäýé Öàãààí õºìñºãò õººíäýé Äóó÷ õººíäýé Õàð õººíäýé Øèâýð õººíäýé Àëàã õººíäýé Õºìðºãèéíõºíèé îâîã Õºìðºã Ãóðãàëäàé õºõçîîò Õººíäýé Õàëèóí õººíäýé Á¿ãýýí õººíäýé Óëààíã¿åý õººíäýé Õàðã¿åý õººíäýé Íàóìàííû õººíäýé Õ¿ðýí õººíäýé Äóóëãàò õººíäýé Áóæìàã õººíäýé Öàãààíõºìñºã õººíäýé Äóó÷ õººíäýé Õàð õººíäýé Øèâýð õººíäýé Õººíäèé Àëàã õººíäèé Õºìðºãèéíõºí Õºìðºã Emberiza aureola Øàð ýëýãò õºìðºã Øàð-ýëýãò õºìðºã 61 Black Redstart Rufous-backed Redstart Daurian Redstart White-winged Redstart НӨ НӨ НӨ НӨ НӨ НӨ НӨ С + + + + Common Nightingale Siberian Rubythroat Bluethroat Siberian Blue Robin Rufous-tailed Robin НӨ НӨ НӨ ДӨ ДӨ НӨ НӨ НӨ ДӨ ДӨ + + + + + Orange-flanked Robin НӨ НӨ Eyebrowed Thrush Pale Thrush Red-throated Thrush Black- throated Thrush Naumann's Thrush Dusky Thrush Fieldfare Thrush Mistle Thrush Redwing Song Thrush Eurasian Blackbird Siberian Thrush НӨ НӨ НӨ НӨ НӨ ДӨ НӨ НӨ НӨ НӨ Т НӨ НӨ НӨ НӨ НӨ НӨ ДӨ НӨ НӨ НӨ НӨ Т НӨ + + + + + + + + + + + + Scaly Thrush НӨ НӨ + НӨ НӨ Bush- Yellow-breasted Bunting + COP9 21 244 10 52 81 60 1 9 457 62 НӨ - Нүүдлийн өндөглөдөг ӨИ - Өвөл ирдэг ДӨ - Дайрч өнгөрдөг С - Суурин Т - тохиолдлын НӨ? - Өндөглөдөг нь бүрэн батлагдаагүй З - Зун тааралддаг, өндөглөдөгүй Нийт 127 2 32 4 23 3 7 198 120 2 35 4 22 1 8 192 177 Annex 2 CMS COP Resolutions links 1-9 List of All COP Resolutions and Recommendations (extract from COP10 Info doc) 10 Bergen, Norway, 2011 - List of Draft Resolutions and Recommendations 9 Rome, Italy, 2008 - List of Resolutions and Recommendations adopted at the COP 8 Nairobi, Kenya, 2005 - List of Resolutions and Recommendations adopted at the COP 7 Bonn, Germany, 2002 - List of Resolutions and Recommendations adopted at the COP 6 Cape Town, South Africa, 1999 - List of Resolutions and Recommendations adopted at the COP 5 Geneva, Switzerland, 1997- List of Resolutions and Recommendations adopted at the COP 4 Nairobi, Kenya, 1994 - List of Resolutions and Recommendations adopted at the COP 3 Geneva, Switzerland, 1991- List of Resolutions and Recommendations adopted at the COP 2 Geneva, Switzerland, 1988- List of Resolutions and Recommendations adopted at the COP 1 Bonn, Germany, 1985 - List of Resolutions and Recommendations adopted at the COP 63 Annex 3 CMS Scientific Council meeting reports links (PDF) English Français Español 16th Scientific Council Meeting Bonn, Germany, 28-30 June 2010 Report of the 16th Meeting of the CMS Scientific Council Activity Planning Meeting Bonn, Germany, 13 June 2009 Report of the Activity Planning Meeting of the CMS Scientific Council 15th Scientific Council Meeting Rome, Italy, 27-28 November 2008 Report of the Fifteenth Meeting of the CMS Scientific Council (Annex VI to COP9 Report) 14th Scientific Council Meeting Bonn, Germany, 14-17 March 2007 Report of the Fourteenth Meeting of the CMS Scientific Council 13th Scientific Council Meeting Nairobi, Kenya, 16-18 November 2005 Report of the Thirteenth Meeting of the CMS Scientific Council 12th Scientific Council Meeting Glasgow, United Kingdom, 31 March - 3 April 2004 Report of the Twelfth Meeting of the CMS Scientific Council 11th Scientific Council Meeting Bonn, Germany, 14-17 September 2002 Report of the Eleventh Meeting of the CMS Scientific Council 64 -x- -x- 10th Scientific Council Meeting Edinburgh, Scotland, Report of the Tenth Meeting of United Kingdom, 2-4 May the CMS Scientific Council 2001 9th Scientific Council Meeting Cape Town, South Africa, Report of the Ninth Meeting of 4-6 November 1999 the CMS Scientific Council 8th Scientific Council Meeting Wageningen, The Report of the Eighth Meeting Netherlands, 3-5 June 1998 of the CMS Scientific Council 7th Scientific Council Meeting Geneva, Switzerland, 1016 April 1997 Report of the Seventh Meeting of the CMS Scientific Council 6th Scientific Council Meeting Bonn, Germany, 1-3 November 1995 Report of the Sixth Meeting of the CMS Scientific Council 5th Scientific Council Meeting Nairobi, Kenya, 4-5 June 1994 Report of the fifth Meeting of the CMS Scientific Council 4th Scientific Council Meeting Bonn, Germany, 17-19 May 1993 Report of the fourth Meeting of the CMS Scientific Council 3rd Scientific Council Meeting Geneva, Switzerland, 9-13 Report of the third Meeting of September 1991 the CMS Scientific Council 2nd Scientific Council Meeting Bonn, Germany, 14-15 March 1991 Report of the second Meeting of the CMS Scientific Council 65 1st Scientific Council Meeting Geneva, Switzerland, 1114 October 1988 Report of the first Meeting of the CMS Scientific Council 66