跳到主要内容
Nelum
尼泊尔的法律

Vulture Conservation Action Plan (2023-2027)

颁布于 2023 · 文本截至 2026-10-01

以研究形式发布的公开法律与官方指引,不构成法律、税务或金融建议。

研究内容本身以英文撰写。标题和标签已翻译,调查结果和引文未翻译。

关于这部法律

语言
English
类型
policy
国家
尼泊尔
主题
Wild species and ecosystems
关键词
capacity building, climate change, ecosystem conservation, endangered species, monitoring, policy/planning, protection of habitats, protection of species, public participation, wild fauna, research, financing, biodiversity

在哪里阅读

文本

所收录的法律原文,按条款排列。每个条款都有自己的链接。

  1. Government of Nepal Ministry of Forests and Environment Department of National Parks and Wildlife Conservation Department of Forests and Soil Conservation VULTURE CONSERVATION ACTION PLAN (2023-2027) Slender-billed Vulture and Indian Vulture, Photo: Ankit Bilash Joshi Government of Nepal Ministry of Forests and Environment Department of National Parks and Wildlife Conservation Department of Forests and Soil Conservation Kathmandu, Nepal 2023 VULTURE CONSERVATION ACTION PLAN (2023-2027) I Technical Team Dr. Ganesh Pant, Ecologist, DNPWC Ms. Sabanam Pathak, Assistant Forest Offi cer, DoFSC Mr. Hem Raj Acharya, Assistant Ecologist, DNPWC Mr. Suman Ghimire, Ranger, DNPWC Dr. Naresh Subedi, Director, NTNC Mr. Ambika Prasad Khatiwada, Senior Conservation Offi cer, NTNC Dr. Kanchan Thapa, Head of Wildlife Programs, WWF Nepal Dr. Bhagawan Raj Dahal, Deputy Country Representative, ZSL Nepal Mr. Krishna Prasad Bhusal, Member, IUCN SSC- Vulture Specialist Group Mr. Ankit Bilash Joshi, Vulture Conservation Program Manager, BCN Mr. Deu Bahadur Rana, Project Offi cer, BCN Mr. Deelip Chand Thakuri, Field Biologist, BCN Review Team Dr. Maheshwar Dhakal, Director General, DNPWC Mr. Devesh Mani Tripathi, Director General, DoFSC Mr. Ajay Karki, Deputy Director General, DNPWC Dr. Ramchandra Kandel, Joint Secretary, MoFE Mr. Man Bahadur Khadka, Former Director General, DoFSC Mr. Hari Bhadra Acharya, Under Secretary, DNPWC Mrs. Ishana Thapa, Chief Executive Offi cer, Bird Conservation Nepal Mr. Chris Bowden, Program Manager, SAVE Dr. John W. Mallord, Senior Conservation Scientist, RSPB Technical Support Bird Conservation Nepal, Uttardhoka, Kathmandu. Published by: Department of National Parks and Wildlife Conservation and Department of Forests and Soil Conservation Babar Mahal, Kathmandu, Nepal. Copyright: ©Department of National Parks and Wildlife Conservation and Department of Forests and Soil Conservation, Nepal (2023) Citation: DNPWC and DoFSC (2023). Vulture Conservation Action Plan (2023-2027). Department of National Parks and Wildlife Conservation and Department of Forests and Soil Conservation, Babar Mahal, Kathmandu, Nepal. Front Cover: White-rumped Vulture, Photo: Ankit Bilash Joshi Back Cover: Red-headed Vulture, Photo: Pratap Gurung II 2037 G overnment of N ep al M inistryrr of Forests & En vir on m en t D ept. of National Parks & Wildl ifeff Co ns er vrr at io n Babarmahal, Kathma ndu Government of Nepal Ministry of Forests and Environment Department of National Parks and Wildlife Conservation FOREWORD Vultures are facing signifi cant threats in Nepal and throughout South Asia, primarily due to the use of non-steroidal an -infl ammatory drug diclofenac and other drugs like nimesulide, ketoprofen and acceclofenac in livestock. These drugs have been found to cause renal failure in vultures, leading to death and signifi cant decline in their numbers. In addi on, deliberate poisoning and electrocu on are also advancing as a threat to the vultures. The Vulture Conserva on Ac on Plan for Nepal 2023-2027 is the result of extensive research and consulta on with stakeholders, including government agencies, non-governmental organiza ons, and community groups. It outlines a range of ac vi es, including monitoring and research, habitat conserva on, advocacy and awareness-raising and veterinary interven ons. The establishment of the vulture safe zone is a signifi cant milestone in vulture conserva on eff orts globally. It serves as a model for other countries facing similar challenges and provides hope for the recovery of vulture popula ons in the region. I fi rmly believe that this ac on plan will make a signifi cant contribu on to the conserva on of vultures in Nepal and help ensure that vultures con nue to play their important role in maintaining a healthy ecosystem. However, the successful implementa on of this plan will require the commitment and coopera on of all stakeholders. I therefore urge everyone to work together to ensure the protec on and survival of these important birds. The DNPWC greatly acknowledges the contribu on of Bird Conserva on Nepal (BCN) for providing fi nancial and technical support to develop this ac on plan and also thank all those who have contributed to the development of this ac on plan. I look forward to working with you all in its implementa on. Finally, I am confi dent that this ac on plan will contribute to long-term existence of the species and its habitat. Maheshwar Dhakal, PhD Director General III Government of Nepal Ministry of Forests and Environment Department of Forests and Soil Conservation ernment of orests and sts an meentenn t r o aeG rereeeeseesesnssment ofanannndndndnd a dd l FFini ooororororororrrrrof Forests & En vi ddd dd d SmSS e EEEEffef f pa FFFFFoFoFFFFoFoent of Forests & Soil Co ns SSSSSSSSSSS a SoS ti o EnEnEnEn Babar Mahal FOREWORD The Vulture Conserva on Ac on Plan (2023-2027) has been me culously cra ed, drawing upon past learning’s and addressing the pressing conserva on challenges faced by vulture species in Nepal. The plan's primary objec ve is to safeguard these species, which are under signifi cant threat due to the use of diclofenac and other harmful NSAIDs in livestock treatment. Recognizing that a substan al por on of the vulture popula on resides outside protected areas, the Department of Forest and Soil Conserva on (DoFSC) fi rmly believes that this ac on plan will play a pivotal role in preserving vulture habitats and ensuring a secure food source for these magnifi cent birds. The engagement of local communi es, par cularly forest user groups, has always been of paramount importance in vulture conserva on eff orts, and it will be further strengthened through the implementa on of the Vulture Safe Zone concept. Given the extensive home range of these creatures, the collabora ve and coopera ve eff orts of all stakeholders are indispensable in ensuring their survival. Consequently, the DoFSC remains steadfast in its commitment to conserving cri cally endangered vultures through ini a ves encompassing rescue and rehabilita on. This ac on plan off ers ample opportuni es to establish a win-win situa on, eff ec vely linking conserva on eff orts with benefi ts for the local communi es. By bolstering the management of community-operated vulture safe feeding sites, for which Nepal has already garnered interna onal recogni on, we can foster a mutually benefi cial rela onship. I am op mis c that our collec ve endeavors will yield success in implemen ng this ac on plan, thus achieving yet another milestone in our vulture conserva on program. Lastly, I would like to extend my hear elt congratula ons to all those involved in the development of this invaluable document. Your unwavering dedica on and commitment are commendable. I eagerly look forward to witnessing the suc cessful outcome of this ac on plan, as it marks a signifi cant stride in our ongoing pursuit of vulture conserva on. Together, let us forge ahead, fostering a harmonious coexistence between vultures and human communi es, thereby preserving the biodiversity and ecological integrity of our cherished natural heritage Devesh Mani Tripathi Director General IV Acronyms and Abbreviations AD Anno Domini before Christ BCN Bird Conservation Nepal BNHS Bombay Natural History Society BS Bikram Sambat (Nepali Calendar Year) BZ Buffer Zone BZCF Buffer Zone Community Forest BZMC Buffer Zone Management Committee CBD Convention on Biodiversity CBO Community-Based Organization CF Community Forest CFUG Community Forest User Group CITES The Convention on International Trade in Endangered Species of Wild Fauna and Flora CNP Chitwan National Park CR Critically Endangered DDA Department of Drug Administration DFD Diclofenac Free District DFO Division Forest Offi ce DoFSC Department of Forests and Soil Conservation DLS Department of Livestock Services DNPWC Department of National Parks and Wildlife Conservation DoA Department of Agriculture GoN Government of Nepal GPS Global Positioning System INGO International Non-Governmental Organization IUCN International Union for Conservation of Nature IVAD International Vulture Awareness Day MoFE Ministry of Forest and Environment NBSAP National Biodiversity Strategy and Action Plan V NP National Park NPR Nepalese Rupee NSAID Non-Steroidal Anti-Infl ammatory Drug NTNC National Trust for Nature Conservation PA Protected Area RSAT Release Site Assessment Tool RSPB Royal Society for the Protection of Bird SAVE Saving Asia’s Vulture from extinction VCAP Vulture Conservation Action Plan for Nepal VCBC Vulture Conservation and Breeding Centre VSFS Vulture Safe Feeding Site VSZ Vulture Safe Zone VU Vulnerable WHO World Health Organization WWF World Wide Fund for Nature ZSL Zoological Society of London Egyptian Vulture adult and chick on nest, Photo: Pratap Gurung VI Table of Contents Acronyms and Abbreviations V Executive Summary 1 Chapter-1 Introduction 3 1.1 Relevance of the Action Plan 3 1.2 Action Plan Development Process 3 1.3 Scope of the Action Plan 3 Chapter-2 Background 4 2.1. Taxonomy 4 2.2 Distribution 5 2.2.1 Global 5 2.2.2 National 5 2.3 Ecology of Vulture 6 2.3.1 Habitats 6 2.3.2 Breeding ecology 6 2.3.3 Feeding ecology 6 2.3.4 Social Behavior 7 2.4 Importance of Vultures 7 2.4.1 Economic Activity 7 2.4.2 Socio-cultural 7 2.4.3 Ecological 7 2.4.4 Human Health 7 Chapter-3 Major Conservation Efforts and Achievements 8 3.1 Conservation Effort 8 3.1.1 Vulture Conservation and Breeding Centre 8 3.1.2 Vulture Safe Zone 8 3.1.3 Safe Feeding Sites 9 3.1.4 Research and Monitoring 10 3.2 Major Achievement 10 3.2.1. Highway Survey 10 3.2.2. Non-Steroidal Anti-Infl ammatory Drugs, NSAID survey 11 3.2.3. Vulture Breeding Ecology 11 3.2.4. Vulture Release 12 3.2.5. Vulture Safe Zone 12 Chapter-4 Conservation Threats 13 4.1 Use of NSAIDs in Livestock Treatment 13 4.2 Habitat Loss and Degradation 15 4.3 Electrocution and Collision 15 4.4 Safe food availability 15 4.5 Poison Baits: Use of Pesticides and other Poisons 15 4.6 Others 16 Chapter-5 Challenges and Opportunities 17 5.1 Challenges 17 5.1.1 Use of Vulture Toxic Drugs on Livestock Treatment 17 5.1.2 Use of Poison Baits on a Carcass 17 5.1.3 Research Gaps 18 VII White-rumped Vulture, Photo: Chungba Sherpa 5.1.4 Legislation 18 5.1.5 Low Level of Public Awareness 18 5.1.6 Coordination Among Stakeholders 18 5.1.7 Lack of Rescue and Release Facility 19 5.2 Opportunities 19 5.2.1 Research and Knowledge Enhancement 19 5.2.2 Tourism Promotion 19 5.2.3 Conservation Breeding Program and Release 19 Chapter-6 Vulture Conservation Action Plan (2023-2027) 21 6.1 Goal 22 6.2 Objectives 22 6.2.1 Prevention of NSAIDs Poisoning and Control the Deliberate Poisoning of Cattle Carcass 22 6.2.2 Promote Scientifi c Research to Enhance Knowledge 22 6.2.3 Release of Captive Vultures into the Safe Environment 23 6.2.4 Promote Safe Food Supply to Vultures 24 6.2.5 Habitat Conservation and Safeguarding from Power Infrastructures 24 6.2.6 Sensitize Stakeholders and Build their Capacity 25 6.2.7 Build Partnership at Local, National, and International Level 26 6.2.8 Strengthen the Vulture Safe Zone 26 Chapter-7 Plan Implementation and Monitoring 27 7.1 Implementing Agency 27 7.2 Financial Plan 28 7.3 Monitoring and Review of the Plan Implementation 28 References 29 Appendix 1: Species Fact Sheet 31 Appendix 2: Logical Framework 40 Appendix 3: Five Year Budget for Vulture Conservation Action Plan 42 VULTURE CONSERVATION ACTION PLAN (2022-2026)VIII Vultures are scavenging birds of prey that eat only dead carrion and play an important role in the ecosystem due to their rapid consumption in the group. Except for Australia and Antarctica, vultures can be found on every continent. Nine of the 16 species of old-world vultures are found on the Indian subcontinent, with six resident species in Nepal. Out of nine vulture species in Asia, four are classifi ed as critically endangered by the International Union for Conservation of Nature. The use of diclofenac medicine for treating livestock is the major cause of the decline of the vulture population. To halt the decline of vultures in Nepal, both ex-situ and in-situ conservation has been practiced. The Government of Nepal banned the production and use of veterinary diclofenac in 2006. In the meantime, promoted the vulture-safe drug Meloxicam subsequently and successfully implemented the fi rst (2009-2013) and second (2015-2019) Vulture Conservation Action Plans for Nepal. Nepal initiated a pioneering idea in the world of working with local communities to establish a Vulture Safe Zone since 2009. As a result, the vulture population especially Critically Endangered Vultures i.e. Executive Summary ............................................................................................ White-rumped Vulture and Slender-billed Vulture are in partial recovery with the declaration of the world’s fi rst scientifi cally validating vulture safe zone. However, vultures are still under high threat due to the use of Non-Steroidal Anti-Infl ammatory Drugs (NSAIDs) other than meloxicam and tolfenamic acid, direct or indirect persecution by humans or poisoning of domestic cattle retaliation against their loss, electrocution, habitat degradation, disturbance by proceeding mine excavation, road construction, river exploitation in and around the vulture nesting sites. The main goal of this Vulture Conservation Action Plan is to restore and maintain the viable wild vulture population in Nepal. The objectives of the action plan are: 1. Prevention of NSAIDs poisoning and control of the deliberate poisoning of cattle carcass 2. Promote scientifi c research to enhance knowledge 3. Release of captive vultures into the safe environment 4. Promote a safe food supply to vultures 5. Habitat conservation and safeguarding from power infrastructures 6. Sensitize stakeholders and build their capacity 7. Build partnerships at local, national, and international levels 8. Strengthen the Vulture Safe Zone Each objective is further detailed with outputs and actions. A total of Nepalese Rupees 148,005,000.00 has been estimated for the plan of fi ve years. The Department of National Parks and Wildlife Conservation bears ownership of the document and collaborates with different stakeholders to ensure the successful implementation of this action plan. VULTURE CONSERVATION ACTION PLAN (2023-2027) 1 I n t r o d ............................................. Himalayan Griffon, Photo: Tashi R. Ghale VULTURE CONSERVATION ACTION PLAN (2023-2027)2 1.1 Relevance of the Action Plan The revision and endorsement of the Vulture Conservation Action Plan (VCAP) 2023-2027 with a well-defi ned strategy is an ultimate need to bridge gaps in the implementation of the previous VCAPs. The Government of Nepal, Department of National Park and Wildlife Conservation (DNPWC) is paramount to implement the conservation actions of wildlife and their habitat in the country. According to the Nepal Biodiversity Strategy and Action Plan (NBSAP), a conservation action plan is an executive guiding tool that stimulate towards the conservation initiation of target species (MoFSC, 2014). Gyps species are one of the threatened species throughout the range. White-rumped Vulture (WRV), Slender-billed Vulture (SBV), Red-headed Vulture (RHV), and Indian Vulture (IV) are categorized as critically endangered species and Egyptian Vulture (EV) categorized as endangered. The u c t i o n ............................................... CHAPTER: 1 vulture conservation actions undertaken in the country for more than a decade resulting the partial recovery of the vulture population in the country. Furthermore, monitoring on use of toxic drugs other than diclofenac, establishment of a Vulture Safe Zone (VSZ), ecological monitoring of vultures, and movement tracking via telemetry tagging is the major initiative to be instigated for long-term conservation of globally threatened vultures in Nepal. 1.2 Action Plan Development Process To revise the VCAP, DNPWC approved the Terms of Reference (ToR) for the preparation of the VCAP. Accordingly, the task force was formed at the DNPWC to prepare a draft of the action plan. The task force prepared a draft action plan based on a literature review, stakeholder discussions, and local consultation workshops. The draft plan was shared with the technical team of DNPWC for their feedback. In addition, a national workshop was organized in Kathmandu to share and get feedback on the draft of VCAP. The draft of the action plan was reviewed by a panel of experts before fi nalizing the action plan. 1.3 Scope of the Action Plan More than a decade of vulture conservation efforts results in the partial recovery of the vulture population in Nepal (Galligan et al., 2020). This conservation action plan emphasizes on strengthen of the Vulture Safe Zone, elimination of toxic NSAIDs and minimize the other threats, the continuation of Vulture Safe Feeding Sites, movement tracking, and understanding of the ecological behaviour of captive released and wild telemetry tagged vulture in coordination with different stakeholders. The vulture conservation action plan encourages regional collaboration with vulture range countries and transboundary dialogue to discourse the different issues. VULTURE CONSERVATION ACTION PLAN (2023-2027) 3 CHAPTER: 2 2.1. Taxonomy Vultures of the world are systematically classifi ed under two families Cathartidae (The New World Vultures) and Accipitridae (The Old World Vultures). Accipitridae vultures include 16 species scattered within nine genera (Aegypius, Gypaetus, Gypohierax, Gyps, Necrosyrtes, Neophron, Sacrogyps, Torgos, and Trigonoceps). Cathartidae vultures include seven species belonging to fi ve genera (Coragyps, Cathartes, Gymnogyps, Vultur, and Sarcoramphus). The major difference between old and new-world vultures is that old-world vultures depend on sight to fi nd food whereas many new-world vultures have a very good sense of smell and can smell dead animals from a distance of up to two kilometers. In addition, Background ............................................................................................ Cathartids differ most conspicuously from Accipitriform in their lack of grasping foot and lack of a syrinx but also in many other important characteristics of skeleton, musculature, feather tracts, moult, internal organs, physiology, sexual dimorphism, and eggshell structure (Ligon, 1967). Nepal supports nine species of vultures from fi ve genera (Aegypius, Gypaetus, Gyps, Neophron, and Sacrogyps) all belonging to the Accipitridae family; namely: White rumped Vulture Gyps bengalensis (WRV), Slender billed Vulture Gyps tenuirostris (SBV), Red-headed Vulture Sacrogyps calvus (RHV), Indian Vulture Gyps indicus (IV), Egyptian Vulture Neophron percnopterus (EV), Himalayan Griffon Gyps himalayensis (HGV), Griffon Vulture, Photo: Deu Bahadur Rana VULTURE CONSERVATION ACTION PLAN (2023-2027)4 Bearded Vulture Gypaetus barbatus (BV), Griffon Vulture Gyps fulvus (GV) and Cinereous Vulture Aegypius monachus (CV). This comprises all species recorded from the Indian Subcontinent (DNPWC, 2015). 2.2 Distribution 2.2.1 Global Vultures are found all over the world except in Antarctica and Oceania. Vulture dwells in diverse ecosystems and geographical ranges from the Amazonian rainforest to the East African savannah, Sahara Desert, and the Himalayas (Buechley & Sekercioglu, 2016). The Old World Vultures are found in Africa, Europe, and Asia while the New World Vultures are found in warm and temperate regions of America. Among the New World Vultures, Black Vulture (Coragyps atratus) and Turkey Vulture (Cathartes aura) are found in both North and South America. Greater Yellow-headed Vulture (Cathartes melambrotus), Lesser Yellow-headed Vulture (Cathartes burrovianus), Andean Condor (Vultur gryphus), and King Vulture (Sarcoramphus papa) are found only in South America and California Condor (Gymnogyps californianus) found only in North America. Among Old World Vultures, four species: Bearded Vulture, Cinereous Vulture, Egyptian Vulture, and Griffon Vulture is found (or had historical range) in all the three continents (Asia, Europe, and Africa). Himalayan Table 1 Resident / Migrant Status, Conservation Status, and Estimated Population of Nine Species of Vultures in Nepal Species* Resident/ Migratory* Conservation Status (Global)+ Conservation Status (Nepal)# Estimated Population in Nepal # Bearded Vulture Resident breeder Near Threatened Vulnerable <500 Cinereous Vulture Winter migrant Near Threatened Endangered 60-100 Egyptian Vulture Resident breeder Endangered Vulnerable 300-1000 Griffon Vulture Passage migrant Least Concern Data Defi cient Himalayan Griffon Resident Breeder Near Threatened Vulnerable <10000 Indian Vulture Rare Visitor Critically Endangered Not Assessed Red-headed Vulture Resident Breeder Critically Endangered Endangered 200-400 Slender-billed Vulture Resident Breeder Critically Endangered Critically Endangered 50-75 White-rumped Vulture Resident Breeder Critically Endangered Critically Endangered <2000 Source: *DNPWC/MoFSC/GoN 2009; +IUCN 2015; #BCN and DNPWC 2011, Inskipp et al. 2016 Vulture, Indian Vulture, Red-headed Vulture, Slender billed Vulture, and White-rumped Vulture are found only in Asia. Additional seven species, Cape Vulture (Gyps coprotheres), Hooded Vulture (Necrosyrtes monachus), Rüppell’s Vulture (Gyps rueppelli), White-backed Vulture (Gyps africanus), White-headed Vulture (Trigonoceps occipitalis), and Palm-nut Vulture (Gypohierax angolensis) are found in Africa. The remaining species, Lappet-faced Vulture (Torgos tracheliotos) is found both in Asia (the Middle East only) and in Africa (Anderson & Mundy, 2001). Presently, 14 of 23 (61%) vulture species worldwide are threatened with extinction and the most rapid declines have occurred in the vulture-rich regions of Asia and Africa (Ogada et al., 2016). All Accipitridae species are protected under the Convention on International Trade in Endangered Species (CITES). 2.2.2 National Among nine species recorded from Nepal, six species are resident, two species are migratory and one species occurs as a vagrant. Five species are currently considered globally threatened, and seven species are considered nationally threatened (Table 1). Detailed species-wise distribution of vultures recorded from Nepal is presented in Appendix 1. VULTURE CONSERVATION ACTION PLAN (2023-2027) 5 2.3 Ecology of Vulture 2.3.1 Habitats Vultures inhibit in areas near human habitation and open areas usually prefer desert, forest, savanna, and grassland for their habitation according to their origin. Some vultures build their nests and breed in cliff whereas some in a tall tree nearby to water sources. 2.3.2 Breeding ecology Old World Vultures (Accipitridae) have low breeding rates (maximum of one egg per clutch) and very slow growth rates (L. Brown & Amadon, 1968). However, BV sometimes lays two eggs per clutch. Vultures are monogamous birds and they pair up for life (Kanaujia & Kushwaha, 2014). If one member of the pairs dies, the other often will take a new mate (Davit, 2009). Vultures normally prefer nesting sites outside of forest edge, grasslands with scattered trees, or found in colonies in a treetop at about 27 meters from the ground level (Rana et al., 2019). Among six resident breeders of vultures recorded from Nepal WRV, RHV and SBV build nests in tall trees. BV and HG build nests on cliffs. EV builds nests in cliffs and occasionally in trees. In Nepal, WRV and HG build nests in colonies while EV, BV, RHV, and SBV nests are found scattered. In Nepal, sometimes SBV and EV nests have been recorded within the WRV colonies. Similarly, BV and HG build nests on the same cliff in the Himalayas. However, RHV is strictly a solitary species. 2.3.3 Feeding ecology All species of vultures recorded from Nepal feed exclusively on carrion. Houston (1984) reported that most of the biomass available to Vultures came from animals. Food is located by soaring in the group which may be composed of either intraspecies or interspecies and considerable aggregations can be formed. Gyps vultures (WRV, SBV, IV, HG, and GV) strictly depend upon the fl esh of carcasses for their food. The diet of BV mainly consists of bones of medium-sized dead domestic Vulture feeding carcass, Photo: Krishna Bhusal VULTURE CONSERVATION ACTION PLAN (2023-2027)6 and wild ungulates ( Brown & Plug, 1990; Margalida et al., 2008). EV is an opportunistic scavenger and feeds on a variety of birds, mammal, amphibian and reptile remains organic rubbish such as rotten vegetable matter; less dependent on large carcasses than other vultures. RHV feeds mostly on carrion. CV mostly feeds on the carrion of birds and mammals, also dead or stranded fi sh (Naoroji & Sangha, 2006). 2.3.4 Social Behavior Vultures are highly social animals with a diverse range of breeding systems both within and among species, ranging from strict territoriality to various forms of social breeding (Christie & Ferguson-Lees, 2010). Their degree of sociality also varies widely irrespective of breeding system, with some species showing permanent forms of group living, whereas others have much more fl uid social systems characterized by fi ssion-fusion dynamics linked to food bonanzas, communal roosting, and other social gatherings (Donázar et al., 1993). 2.4 Importance of Vultures Vultures are the natural scavenger, most notably the disposal of carrion, especially livestock carcasses. These services have an impact on economic activity, sociocultural aspects, environmental quality, and human health. 2.4.1 Economic Activity When livestock dies in rural areas, in the absence of vultures, locals or local authorities must either accept the disamenity of the stench of rotting fl esh and the increased disease risks or incur the costs of carcass disposal (e.g. by burial or incineration). Even in areas where dogs have increased considerably, they do not remove the need for carcass disposal because there are often insuffi cient dogs; and, as they are not such effi cient scavengers, they leave part of the carcass unscavenged. This will ultimately have a direct impact on human health. Other important benefi ts society receives from the protection of vultures derive from the pleasure people might receive by viewing them. For example, some ecotourism companies include the possibility of seeing vultures within their itineraries, and several tour operators offer bird watching tours specifi cally to see vultures. Tourism attracted by viewing vultures generates additional income for sectors, which supply the tourism industry. For example, the Vulture safe feeding sites of Nawalparasi and Kaski districts, Nepal. The values placed on vultures may also include values on the option of viewing or bequest values for future generations. 2.4.2 Socio-cultural Vultures have different aspects of belief based on different cultures and religions. They also have an important cultural role in the consumption of human corpses in sky burials within Nepal and Tibet. Sky burial is one of the ancient cultures of Buddhism in the high Himalayas of the Tibetan Plateau, also among Zoroastrians in the Parsi communities of India. Vultures, in this context, are symbolized or associated with purifi cation and rebirth (Eldar, 2008). Furthermore, In the Hindu religion, animals, birds, and snakes are considered important for human existence, and within Hindu mythology, the vulture God Jatayu is regarded as a holy bird. Jatayu gave up his life while attempting to protect Sita, wife of Rama. Vultures are the spy of “God Sani” (Saturn) and are epitomized as the symbol of bravery in the famous Holy book Ramayana. 2.4.3 Ecological Vultures play an essential role in maintaining a healthy ecosystem. Vultures are the most effi cient scavenging birds and play a highly important ecological role through the rapid consumption of animal carcasses (Ogada et al., 2016). As carrion specialists, the absence of vultures from carcasses may affect the community composition of scavengers at carcasses, which could alter scavenging rates for individual species. In localized regions where vultures are functionally extinct, the absence of vultures at carcasses appears to have driven a rapid increase in the abundance of opportunistic species such as feral dogs and rats (Pain et al., 2003; Prakash et al., 2003). Therefore, vultures play an important role in decomposing carcasses, maintaining community structure, and moderating contact between mammalian scavengers at carcasses. 2.4.4 Human Health An increase in uneaten livestock carcasses may pose a direct threat to human health because they provide a breeding ground for pathogenic bacteria leading to the possibility of direct or indirect infections. As such, these carcasses can be sources of a range of infectious diseases, such as anthrax (George et al., 1994; John, 1996; Vijaikumar et al., 2002). In removing carcasses rapidly and effi ciently, vultures clean the environment and help protect humans, livestock, and wildlife from infectious diseases. A fall in the vulture population could increase the dog population (Prakash et al., 2003). VULTURE CONSERVATION ACTION PLAN (2023-2027) 7 CHAPTER: 3 3.1 Conservation Effort Vulture conservation in Nepal was initiated in early 2000. There was ignorance of the issue and the solutions across government, civil society, and the private sector. The sheer geographical scale of the problem and how to work across such huge areas brought its challenges. Since 2002, our vulture recovery programme initiated an integrated approach, which involves advocacy, education, monitoring, research, captive breeding, supplementary feeding, and site protection to help implement Nepal's Vulture Conservation Action Plan. DNPWC in collaboration with DDA, BCN, NTNC, RSPB, and ZSL endorsing a ban on the production and use of a veterinary drug, diclofenac in 2006 and promoting the vulture safe drug, Meloxicam subsequently. Furthermore, realizing the rapid decline of the wild population and the urgent need to establish breeding centers, DNPWC established a Vulture Conservation and Breeding Centre (VCBC) at Kasara, Chitwan in 2008 aiming to conserve vulture species. The Major conservation efforts are described below. 3.1.1 Vulture Conservation and Breeding Centre Due to the rapid decline of South Asian vultures, there is an urgent need to establish vulture breeding centers to protect them from extinction. As a result, BCN, NTNC, RSPB, and ZSL aided DNPWC, Government of Nepal, in establishing the VCBC at Kasara, Chitwan, Nepal, within Major Conservation Efforts and Achievements ............................................................................................ the Chitwan National Park in 2008. The goal of the program is to save two Gyps species, WRV and SBV. With two breeding aviaries and two holding aviaries adjacent to the Gharial Breeding Centre, the breeding centre covers 6,375 square meters. In total, 60 juvenile WRV were captured as fl edglings in the wild in Nepal’s western regions and placed in two colony aviaries in VCBC, Chitwan. These birds were transferred from holding aviaries to the large colony to prepare for breeding in a mimic of natural habitat with ponds for bathing, perches that mimic tree branches, hammocks for nesting and laying egg, and shades for relief from the scorching heat. The large colony is designed with a 120-meter span, which encourages the birds to fl y freely from one end to the other. A total of 18 chicks were hatched in VCBC since its establishment in 2008, indicating that the initiative has been a success. All of the captive-bred chicks, as well as the captive reared adults have been released with a satellite tag from the center. 3.1.2 Vulture Safe Zone In 2009, Nepal pioneered the concept of establishing a Vulture Safe Zone (VSZ) working with local communities. A VSZ is an area surrounding one or more wild vulture nesting colonies, large enough to encompass the mean foraging range (>30,000 km2) completely free from diclofenac use. This VSZ concept arose from some VULTURE CONSERVATION ACTION PLAN (2023-2027)8 excellent conservation efforts to create diclofenac-free zones across the country utilizing a district by district, province by province approach. There are three provisional VSZs (pVSZs) in Nepal centered around Pithauli (Nawalparasi), Bijauri (Dang) and Khutiya (Kailali) VSFS. Approximately 30 nesting colonies of vultures (largely white-rumped vulture, and other resident breeders) are protected within these pVSZs. VSZ is an innovative way to ensure that these threats are minimized, and favourable conditions have been maintained to create a scientifi cally validated VSZ. A total of 76 districts been declared as a DFZ out of 77 districts till 2021 with coverage of 146,454 sq. km (BCN, unpublished). These are verifi ed through declaration certifi cates and monitoring reports. DNPWC in partnering with Bird Conservation Nepal (BCN) along with vet professionals, other conservation organisations, and government agencies has been regular partnering with communities within potential VSZs to completely stop the diclofenac use and other threats to vultures before declaring the area as VSZ. In the beginning, the big challenge was removing diclofenac from the veterinary system. Since 2009, BCN has been working with local people to establish a Vulture Safe Zone in order to advocate for a diclofenac ban and to maintain a captive population of vultures in Nepal (Paudel, 2013).The districts are declared as DFZs once diclofenac levels in veterinary pharmacies are monitored and the absence of diclofenac in the district is proven. The BCN, in collaboration with its local partner in stewardship of district-level government agencies and District Livestock Service Offi ce, coordinates this program. pVSZs are considered full VSZ status only after it is proven that the primary threat to vultures has been eliminated for that two years of pharmacy monitoring data with no veterinary diclofenac found and no dead vulture should be found with diclofenac poisoning at least for fi ve years or no diclofenac residue to be found in more than 800 cattle carcass or through satellite tagging of 25 vultures for two years and doing the post mortem of the carcass to identify the cause of death. 3.1.3 Safe Feeding Sites Nepal is the fi rst country in the world to conceptualize a community-based Vulture Safe Feeding Site, which provides safe food within a Vulture Safe Zone to promote community support and long-term sustainability (Bhusal, 2018). The world’s fi rst community-managed Vulture Safe Feeding Site (Jatayu Restaurant) was established in 2006 at Kawasoti, Nawalparasi and similar efforts have been replicated in six other sites in Nepal. These Vulture Restaurants collect old and unproductive cows from nearby villages and reared for at least seven days to ensure that they are diclofenac-free and then fed to vultures after their natural death. The VSFS is the area surrounding one or more wild vulture nesting colonies Vulture feeding carcass in Safe Feeding Site, Photo: Ankit Bilash Joshi VULTURE CONSERVATION ACTION PLAN (2023-2027) 9 that is large enough to encompass the mean feeding range and is diclofenac-free. VSFS is commonly known as Vulture (Jatayu) Restaurant, a site where vultures are provided safe food while considerable efforts are made to free the prevalence of diclofenac. In Nepal, seven VSFS are in operation, with the primary objectives of providing safe food for vultures and integrating local communities to enhance their livelihoods. Communities benefi t from activities that generate income and connect them together. This neatly integrates biodiversity conservation with a source of revenue. Vulture Restaurants’ surrounding villages developed a clear and strategic plan to save vultures and other wildlife by implementing sustainable living practices in rural communities. The goal was for these places to become model sustainable conservation and eco-tourism zones, demonstrating how people may not only survive, but also develop and thrive while conserving and maintaining the environment in which they live. 3.1.4 Research and Monitoring Annual road transect survey follows east-west highway and covers most of the hilly areas of Karnali, Lumbini, and Gandaki provinces. This transect was established since the massive vulture falling-off in the country, the survey revealed the loss of White-rumped vulture and Slender-billed Vulture with 91% and 96% respectively in the country (Chaudhary et al., 2012). Since the mass decline of vultures was confi rmed with the widespread use of diclofenac, the NSAID monitoring is being under taken in two different methods such as General and Undercover survey as a result of zero availability reckon to declaration of Diclofenac Free Districts. Annual breeding success of vulture is determined by the three visits of nest monitoring in each breeding season adding on vulture population, nesting, and foraging and feeding sites exploration and monitoring activities in various potential locations. Adding on, Nepal has released captive and wild White-rumped vulture in the wild to ensure the survival rate of the vultures with identifying the threats and their favorable habitat. Similarly, BCN has initiated Vulture Count Campaign since 2019 on the occasion of International Vulture Awareness Day (IVAD) following the same time interval on the same day method throughout the country annually. 3.2 Major Achievement 3.2.1. Highway Survey Not long after the catastrophic declines in vulture populations began, started monitoring vulture species throughout Nepal using major roads as a series of transects along which vultures have counted with 14 years of data illustrate and increase in White-rumped and Slender-billed vultures. The study shows population of two critically endangered Gyps vultures decline between 2002 and 2012/13 followed by partial recoveries between 2012/13 and 2018. 1.6 1.4 1.2 1.0 0.8 0.6 0.4 0.2 0.0 2002 2004 2006 2008 2010 2012 Year In de x 2014 2016 2018 2020 Figure 2: Annual index values for populations of White rumped (WRV: fi lled circles) and Slender billed (SBV: open circles) Vultures in Nepal for 2002–2018, relative to 2002. Vertical lines for the WRV points are 95% confi dence intervals from the quasi-Poison model. Curves show results from the fi tted piecewise log-linear regression models for WRV (solid line) and SBV (dashed line). Crosses in the upper part of the diagram show the estimated breakpoints and their 95% confi dence intervals. (Galligan et al., 2019) VULTURE CONSERVATION ACTION PLAN (2023-2027)10 3.2.2. Non-Steroidal Anti-Infl ammatory Drugs, NSAID survey Over a decades of NSAIDs survey shows virtually no prevalence of diclofenac in veterinary pharmacies and an increase in sales of meloxicam and few evidence of Tolfenamic acid (the vulture-safe alternative to diclofenac). However, the availability of NSAIDs other than diclofenac such as Nimesulide, Ketoprofen, Flunixin and Acceclofenac that have been proven as vulture toxic nurture serious threat in future. Strong advocacy work on vulture conservation and educating communities on the vulture-toxic-NSAIDs problem were important factors behind these achievements. The aim was to rid Nepal of diclofenac and prevent other vulture-toxic NSAID from taking its place. Thus, 76 of 77 districts of Nepal has been declared as the Diclofenac Free District. This was achieved through a programme of wide engagement with communities, local decision-makers and authorities, veterinarians and farmers, conservation organizations, and national media outlets. Nepal has swapped meloxicam for diclofenac, managed Vulture-Safe Feeding Sites, developed vulture ecotourism, and highlighted the importance of vulture role and their ecosystem services. It is these activities, on the back of the ban, which has truly benefi tted Nepal’s vultures. 3.2.3. Vulture Breeding Ecology Systematic and continuous ecological monitoring of WRV in Nepal was started in 2008 primarily in and around the VSFS, Nawalpur. Continuing the ecological monitoring of vulture in different district of Nepal results in the absolute number of active nests are increasing in recent years (Figure 3., Rana et al., 2019). All six resident vultures breeding ecology have been monitored throughout the country with 68.8% breeding success in 2020/21 breeding season whereas the breeding population of Critically Endangered SBV and RHV nesting sites is yet to be explored in wide range of its potential distributional range. 0 2008 2009 2010 2011 2012 2013 2014 Year Breeding Success (%) Su cc es s Ra te 2015 2016 2017 2018 2019 2020 2021 10 20 30 40 50 60 70 80 90 Figure 3: Breeding status of WRV in Nepal fi rst captive White-rumped Vulture chick breed in wild, Photo: Deu Bahadur Rana VULTURE CONSERVATION ACTION PLAN (2023-2027) 11 3.2.4. Vulture Release Nepal has released a total of 119 White-rumped Vultures in the nature since 2017-22 in six different events with telemetry tagging (Figure 4). These vultures are released in 1:1 ratio of wild and captive (captive-bred and captive reared) vultures. The data received from the released vultures have made the pleasing movement preferably west and northern Mid-hills to the south, India from the release site. This information has great impact on identifying the roosting, nesting and foraging sites in different parts of the country. Trans boundary collaboration on vulture conservation with India has greatly improved not only between conservation bodies but at the government offi cial level as the vulture roam far and wide and does not know international boundaries. Furthermore, it is great to welcome the new chicks hatched from the Captive reared White-rumped Vulture. Monitoring the movement and behavior of vulture fi tted with the GPS Telemetry tagged was initiated in Nepal since 2013. Moreover, three Red-headed Vultures, three Himalayan Griffon are fi tted with GPS telemetry tagged in 2014 and 2019 respectively. In total 11 BV were tagged and monitored (Subedi et. al., 2020). 0 2017 2018 2019 2021 Year Captive Wild Vu ltu re N um be r 2022-Mar 2022-Nov 2 4 6 6 8 10 12 14 11 12 9 13 10 8 10 10 10 1010 Figure 4: Number of telemetry tagged captive released and wild White-rumped Vultures 3.2.5. Vulture Safe Zone Gandaki- Lumbini Vulture safe zone was scientifi cally approved and declared as the true VSZ at the 11th annual meeting of SAVE, based on extensive pharmacy survey over a long period in which no diclofenac found in the market. There was no evidence that any birds died of NSAID poisoning. The high survival rates of wild birds, especially adults, and the lack of evidence for NSAID caused mortality, suggest that vulture habitat in the Nepal VSZ is virtually free from diclofenac and that other hazards. Darchula Bajhang Humla Mugu Dopla Mustang Myagdi Manang Lamjung Tanahu Nawalpur Parasi Gorkha Dhading Nuwakot Rasuwa Sindhupalchok Kavre Kathmandu Bhaktapur LalitpurMakwanpur Parsa Bara Rautahat Sarlahi Mahottari Sindhuli Ramechhap Dolkha Solukhumbu Sankhuwasabha BhojpurKhotang Okhandhunga Udaypur Siraha Saptari Sunsari Morang Jhapa Ilam Dhankuta Taplejung Panchthar Tehrathum Dhanusha Chitwan Kaski Parbat Syanja Palpa Rupandehi Baglung Pyuthan Arghakhachi Kapilbastu Gulmi Jajarkot Rukum West Rukum East RolpaSalyan Dang Banke Jumla Kalikot Dailekh Surkhet Bardiya AchhamDoti Kailali BajuraBaitadi Dadeldhura Kanchanpur Vulture Safe Zone Diclofenac Free District Figure 5: Vulture Safe Zone and Diclofenac Free Districts in Nepal VULTURE CONSERVATION ACTION PLAN (2023-2027)12 4.1 Use of Vulture Toxic NSAIDs in Livestock Treatment The widespread veterinary drug, diclofenac used to treat livestock suffering from pain and infl ammation were premeditated as the primary means of the catastrophic CHAPTER: 4 Conservation Threats ............................................................................................ decline of the vulture population resulting in severe danger of extinction from their distribution ranges in past decades (Harris, 2013; Oaks et al., 2004). The government of Nepal including other South Asian countries banned on production and use of harmful NSAID diclofenac and instead promoted Meloxicam, a safe alternative drug. VULTURE CONSERVATION ACTION PLAN (2023-2027) 13 20 2012 2013 2014 2015 Year Western Pahad Western Terai Eastern Terai Pe rc en ta ge o f N SA ID s al es th at w er e ni m es ul id e 2016 2017 18 16 14 12 10 8 6 4 2 0 Now the use of vulture toxic drug diclofenac highly reduced in the region (Galligan et al., 2020). However, diclofenac is not the only NSAIDs responsible for vulture toxic and thereby killing vultures. Recently, the evidence for toxicity to vulture further six NSAIDs other than diclofenac has been scrutinized namely ketoprofen, nimesulide, aceclofenac, carprofen, phenylbutazone, and fl unixin. These NSAIDs are competing with meloxicam for diclofenac’s former market share, posing a major threat to Asia’s critically endangered vultures’ recovery. 8 7 6 5 4 3 2 1 0 2010 2011 2012 2013 2014 2015 2016 YEAR Total Incidents NU M BE R OF IN CI DE NT S 2017 2018 2019 2020 2021 2022 Figure 5: Percentage of pharmacies that sale nimesulide during covert (undercover) surveys of pharmacies in three regions of Nepal from 2012 to 2017. Figure 6: The trend of electrocution and collision incidents of vulture in Nepal Electrocution of Himalayan Griffon, Photo: Deu Bahadur Rana VULTURE CONSERVATION ACTION PLAN (2023-2027)14 4.2 Habitat Loss and Degradation In Nepal, various developmental activities are being undertaken as a result the natural habitat of different wildlife including the birds are severely disturbed and are forced to shift from their historic habitation to other best alternate locations. Road construction, mine excavation, tree felling, river exploitation, and other development activities nearby vulture colony are the major threats to vulture which has the direct impact on long-term survival. The Terai Arc Landscape (TAL) of Nepal is a key habitat for the WRV, with around 85 percent of the species’ nests in the nation (Rana et al., 2019). Bhusal et al., 2020 estimated that 12.71 percent of total areas of TAL are currently appropriate for WRV and predicted that in the next 50 years, this suitable habitat will have fallen to 11.57 percent, i.e. 9 percent of current suitable habitat will be lost from the TAL area. In general, it is clear that habitat loss is not a direct threat to vultures. However, these various identifi ed habitats should be prioritized for regular monitoring and management for sustainable recovery of such critically endangered species critical habitat that will disappear in the future if conservation initiatives are not implemented. 4.3 Electrocution and Collision Electrocution from electricity and other residential lines has always posed a major threat to large fl ying birds. Above ground power lines (both medium voltage distribution lines and medium to high voltage transmission lines) present potentially fatal risks for birds through risks of collision with overhead wires and the risk of electrocution. The trend of the electrocution incident is increasing in the later years. As the developmental works has been increasing in Nepal, these incidents may even rise in number causing a great threat to vulture population that have just started to revive in the wild. 4.4 Safe food availability Localised food scarcity is also becoming threat to vulture whereas the livestock rearing practices is decreasing. The livestock herding trend is decreased to approx. 50% than previous decades in the country and the majority of herders follows burying as the carcass disposal mechanism. Thus, burying carcasses might be one of the likely causes of a future localized food scarcity for vultures. 4.5 Poison Baits: Use of Pesticides and other Poisons Agriculture and livestock herding practices are the major occupations in Nepal. Human-wildlife confl ict is the major threat throughout the country resulting in retaliatory killing with various practices such as trapping, poisoning, pesticides use, etc. thus the additional mortality of vultures from secondary poisoning can harm the small vulture population (Margalida et al., Mass death of vultures due to feeding of poisoned bait carcass, Photo: Deu Bahadur Rana VULTURE CONSERVATION ACTION PLAN (2023-2027) 15 120 Carcass Poisoning Electrocution Human Persecution Cause Nu m be r Nest Falling Disease Unknown 100 80 60 40 20 0 Figure 8: Cause of vulture death in Nepal from February 2010 to June 2019 (Chaudhary et al., 2019) 2014). In Nepal, a total of 211 vultures were reported victimized to death by the consumption of the poisoned carcass from the year 2010-2021 (BCN unpublished). Twenty-two vultures have been rescued and under treatment 14 of them were successfully released back. The population-level impact of poison-related mortalities of poorly understood vultures in Nepal. 4.6 Others There are other occasional intentional and unintentional anthropogenic activities such as teasing the bird as entertainment, targeting by the catapult which can result in mortality. These are not generally thought to be a signifi cant problem, but can be addressed by general awareness raising of the important role vultures play in the ecosystem. The eventual recovery of the Vulture population in Nepal may have threatened by toxic NSAIDs, unintentional poison baits, nest falling, human persecution, habitat loss, localized shortage of food, electrocution, diseases (Chaudhary et. al., 2019, Bhusal, 2018). 2010 2011 2012 2013 2014 2015 2016 2017 2018 2019 2020 2021 2022 Death Released Treatment 80 70 60 50 40 30 0 20 10 0 Year Nu m be r o f V ul tu re s 24 28 0 0 0 0 0 1 11 29 13 9 13 19 34 71 Figure 7: Number of vulture reported from Poison baits incidents VULTURE CONSERVATION ACTION PLAN (2023-2027)16 CHAPTER: 5 Challenges and Opportunities ............................................................................................ 5.1 Challenges 5.1.1 Use of Vulture Toxic Drugs on Livestock Treatment The catastrophic decline of Gyps species across the Indian Subcontinent means that many other scavenging birds are also exposed to contaminated carcasses. Non Steroidal Anti-Infl ammatory Drug (NSAID), diclofenac has been subjected to a primary consequence of ecological disaster on the Asian vulture population. Despite the wide range of compounds belonging to this family of drugs available in the worldwide market, to date, beside diclofenac other six NSAIDs- namely ketoprofen, nimesulide, aceclofenac, carprofen, phenylbutazone, and fl unixin have been tested for the toxicity on vultures of the Gyps genus under controlled conditions. Meloxicam has proven safe for vultures when used in cattle with a result of 0.5 hours against the 12 hours in diclofenac, meaning the activity of meloxicam is practically innocuous to vultures one hour after it’s been inoculated whereas diclofenac is still active 24 hours after treatment (Fourie et al., 2015). Recent study has identifi ed tolfenamic acid as the second confi rmed vulture safe NSAID after meloxicam (Chandramohan et al., 2022) However, diclofenac, ketoprofen, aceclofenac, nimesulide, and fl unixin have already proven fatal for vultures in the wild whereas the effect of other NSAIDs was merely seen during toxicity trials. The study reveals the availability of diclofenac in Nepal accounts for almost zero while other eleven different NSAIDs were recorded, several of which are known or suspected to be toxic to vultures (Galligan et al., 2020). Nimesulide has emerged as a fast-growing threat in Nepal and threatens to undermine the progress with removing diclofenac. Therefore some proactive steps are urgently required to address this. The lack of adequate safety testing of other NSAIDs on Gyps vultures to identify safe and toxic drug and prevent harm from other potential risks different pharmaceutical products used for livestock treatment instinct the serious poisoning challenges on vulture and other wildlife population. 5.1.2 Use of Poison Baits on a Carcass Mortality resulting from illegal poisoning has unique characteristics that make its surveillance and the effects Examination of dead vultures, Photo: Ishwari Prasad Chaudhary VULTURE CONSERVATION ACTION PLAN (2023-2027) 17 on the population somewhat different from other anthropogenic causes of mortality (Martínez-Haro et al., 2008). Vultures are obligate scavengers and are therefore vulnerable to poisoning particularly at carcasses that are laced with poison deliberately to kill terrestrial carnivores. Accidental or secondary poisoning is one of the greatest issues in Nepal in preserving the remaining small population of vultures. Illegal poisoning has been documented as the detrimental effects on population dynamics, especially in those long-lived species with low reproductive rates and delayed maturity (Margalida et al., 2014) thereby vultures are susceptible to the introduction of toxicant in the food chain that anticipates towards severe extinction in future. 5.1.3 Research Gaps In Nepal different level of research on megafauna including vulture have been undertaken however, it lacks the intensive exploration of potential vulture breeding and feeding sites, laboratory-based test to identify the actual cause of vulture death, corpse test to ensure antibiotic resistance level, level of food competition with other trophic carnivores as the major research gap which is crucial to address in the future conservation programme. 5.1.4 Legislation Vulture serves the ecosystem by consuming a large mass of carrions and prevents the environment from the spread of different communicable diseases transmitted by various wild and domestics animals. The population of the vulture was decline alarming to the extinction. It is unfortunate that these invaluable Gyps species still lack to enlisted on nationally protected species. NPWC Act 1997 has ascertained punishment on delinquents against illegal hunting of wildlife and birds but there is no rigorous procedure for immediate punishment. To ban on the use and production of various detrimental NSAIDs which are available in the market whilst the major challenges for long-term vulture conservation. 5.1.5 Low Level of Public Awareness Numerous incidents of capturing and entertaining with a vulture, hitting them with the catapult, and sometimes killed due to the miss identifi cation between raptors and vultures against retaliation against the loss of their chicken or even small ungulate in different locations within the country. The protection and understanding of vultures remain insuffi cient nationwide, and there is a lack of adequate punishment for harming them. Moreover, public awareness regarding superstitions, myths, and irrational beliefs surrounding vultures needs improvement to discourage such harmful practices. 5.1.6 Coordination Among Stakeholders Vulture conservation in Nepal is a long-term conservation programme that aims to reach a broader level of national and international stakeholders. One of the challenges in vulture conservation is the less coordination among stakeholders. To address this issue, it is crucial to establish a shared vision and goals for vulture conservation that take into account the perspectives Road Transect Survey of Vultures, Photo: Ankit Bilash Joshi VULTURE CONSERVATION ACTION PLAN (2023-2027)18 and needs of all stakeholders. This can be done through stakeholder engagement, consultation, and participatory decision-making processes. Effective communication and information sharing are also essential to ensure that all stakeholders are informed and involved in conservation efforts. In addition, it is important to recognize and respect the rights and interests of local communities and indigenous peoples, who may have traditional knowledge and practices related to vulture conservation. 5.1.7 Lack of Rescue and Release Facility Vultures are found injured or grounded in various locations across the country, however only a limited number of injured vultures are rescued and treated. The successful and timely injured vulture rescue may affect due to the unskilled bird handling technique, lack of information, inaccessible demographic features. The rescued birds require ample rehabilitation facilities where the rescue and treatment center of vulture lacks in the country. 5.2 Opportunities 5.2.1 Research and Knowledge Enhancement The distribution of the vulture population is well understood throughout the country however in depth research on understanding the movement and breeding ecology, the sympatric relationship between scavenging birds of prey, vulture, and trophic carnivore is the key potential theme that has yet to be explored. Furthermore, it is also very crucial to conduct research based on laboratory tests to understand the different aspects of medical examinations and make the vulture conservation programme successful. 5.2.2 Tourism Promotion Nepal withstands as one of the famous tourist destinations due to its unannotated landscape beauty, wilderness, wildlife, and cultural diversity. The country holds all nine vulture species found in the Indian Subcontinent, offering a unique and enriching experience for tourists seeking refreshment, satisfaction, and opportunities for research and entertainment. Currently, vulture safe feeding sites are the well-known vulture tourism destination in Nepal however, vulture tourism linking with other wildlife and cultural tourism has the ample opportunity to promote tourism and strengthen the community livelihood standards. 5.2.3 Conservation Breeding Program and Release Nepal has made signifi cant strides in vulture conservation through both in-situ and ex-situ programs, resulting in a partial recovery of the vulture population. However, further efforts are needed to intensify conservation practices. Creating vulture safe zones and safe feeding centers is crucial to address the challenges of low breeding capacity and food scarcity in the wild. GPS telemetry tagging aids in studying vultures for future conservation. Monitoring released and wild-tagged vultures in VSZ is essential. Scaling up tagging techniques enhances broader research for vulture conservation Tourist watching vultures in safe feeding site, Photo: Kewal Pd. Chaudhary VULTURE CONSERVATION ACTION PLAN (2023-2027) 19 VULTURE CONSERVATION ACTION PLAN (2023-2027)20 Vulture Conservation Action Plan (2023-2027) CHAPTER: 6 Egyptian vulture, Photo: Prem Bahadur Bamjan VULTURE CONSERVATION ACTION PLAN (2023-2027) 21 6.1 Goal Restore and maintain the viable wild population of vultures in Nepal 6.2 Objectives Maintain viable wild populations of all the species of vultures through the provision of safe food and maintenance of suitable habitats. 6.2.1 Prevention of NSAIDs Poisoning and Control the Deliberate Poisoning of Cattle Carcass Rationale Ketoprofen, Aceclofenac, and Nimesulide have been found toxic but are still not banned from the country. Meloxicam and tolfenamic acid is the only known vulture-safe NSAID, yet there are other NSAIDs available potentially vulture toxic. There is still no regulatory mechanism that exists to ban NSAIDs shown to be vulture toxic. The poisoning of vulture food by NSAIDs continues to be a pressing problem for vulture conservation in the country. Deliberate or unintentional poisoning on cattle carcasses also causes mortalities in vultures. Though occasional incidences are found now, it could become a serious problem for vulture conservation causing local extinction. Easily available the potent agricultural pesticides in the market is also one of the major problems in mortality. Outputs 1. Ban on vulture toxic NSAIDs like Acceclofenac, Ketoprofen, Nimesulide, and other toxic compounds. 2. Vulture-safe NSAIDs like Meloxicam and Tolfenamic acid available on market. S.N. Actions 1 Advocate a ban on Acceclofenac, Ketoprofen and Nimesulide 2 Advocate on the effi cient regulatory mechanism to ban other NSAIDs shown to vulture-toxic and carcass poisoning. 3 Effective monitoring of import and distribution of NSAIDs / toxic drug and monitoring of drug prescribers. 4 Safety testing of recently introduced and upcoming NSAIDs for vultures. 5 Research on Antimicrobial sensitivity tests to monitor the antibiotic resistance in vultures and access the impact on human health. 6 Engage agencies and organizations working in the Nepal-India border area to remove multi dose vials of diclofenac. 7 Continue to raise awareness of the vulture toxic, vulture-safe NSAIDs and Incidental poisoning. 8 Ensure sale of veterinary NSAIDs only on prescription and regulating the use of easily available potent agriculture pesticides. 9 Promote other NSAIDs proven to be vulture safe and of good quality. 10 Collection of dead vultures and conduct post mortem examination to fi nd the causes of mortality. 11 Awareness – Vets/Para vets and local vet practitioner (Restraining/ First aid/ Sample collection & dispatch to the laboratory. 12 Establishment of rescue Center at each Provincial level. 13 Strengthening of laboratory for diagnosis/ research of toxicological cases in vultures. 14 Creating Database of poisoning incidences 15 Development of fi eld level diagnostic protocols for effective diagnosis of health problem 6.2.2 Promote Scientifi c Research to Enhance Knowledge Rationale Conservation actions need to be based on evidence and evaluate and adapted through monitoring. Knowledge of vulture biology and ecology is still limited and the fi ndings from the research and monitoring are not always disseminated widely. Regular monitoring of the vulture populations needs to be continued every year to know the population trend and effectiveness of the conservation efforts. Outputs 1. Science-based information system documented. 2. Central database on all vulture species available. VULTURE CONSERVATION ACTION PLAN (2023-2027)22 S.N. Actions 1 Regular monitoring of vulture populations using road transect surveys. 2 Regular vulture count all over the country. 3 Nest monitoring for vulture population breeding success. 4 Monitor NSAID availability in veterinary pharmacies through open and undercover surveys. 5 Monitor NSAID prevalence in livestock and vulture carcasses. 6 Continue satellite tagging of all the captive released vultures. 7 Capture and tag the wild vultures 8 Continue monitoring, tracking, and ground truthing of tagged vultures, recover the corpses and establish the cause of death. 9 Expand knowledge on vulture biology and ecology. 10 Expand expertise in the fi eld, lab, and desk based science. 11 Assemble and maintain a central database. 12 Produce reports, articles, and other media for dissemination among a varied audience. 13 Engage and support communities in nesting sites and tree protection. 14 Include RHV, SBV, and WRV in the list of protected birds. 15 Secure long-term funding and sustainable practice for in-situ activities. 6.2.3 Release of Captive Vultures into the Safe Environment Rationale Captive vulture in the Vulture Conservation and Breeding Center will be reared, bred, and utilized for the reintroduction of vultures in the wild. Captive vulture from VCBC will be transferred to Pre-release aviary made in release site and encourage them to interact with the wild for not more than six months where the soft release will be done. Before the birds are released in the wild, it will be satellite tagged and ensured that the habitat from the release site is safe for the vulture. Assuming releases proceed and the environment remains suffi ciently safe Captive release White-rumped Vulture, Photo: Jyotendra Jyu Thakuri VULTURE CONSERVATION ACTION PLAN (2023-2027) 23 for their survival, the remaining birds from the breeding centre will all be released by 2023 and the vulture centre will be closed or converted for other purposes thereafter. Output 1. Successful survival of captive vulture around VSZ. S.N. Actions 1 Continue to release captive-bred vultures when less than 2 years old and also release other birds by maintaining best-breeding birds annually and fi nally release all the captive birds by 2023 2 Continue satellite tagging of all the captive released vultures. 3 Develop VCBC into Vulture Research Center. 4 Create Emergency Fund for crisis management including disease outbreaks. 5 Periodic staff training and skill development 6 Secure long-term funding 7 Regular ground-truthing of the released vulture. 8 Safety and Hygiene evaluation of the release site 6.2.4 Promote Safe Food Supply to Vultures Rationale Vultures are free-ranging and fi nd their food sighting from a long distance and consume a large mass of carcasses in a short interval. In the past decades due to the use of veterinary drugs diclofenac large mass of vulture’s wake were suffered from visceral gout leads to their immediate death. Carcass disposal by burying could be one of the possible reasons for a localized shortage of food for vulture in the future. Furthermore, the cause of vulture decline ensues intentional and unintentional poisoning of vultures. Output 1. Available of Safe food supply to vultures. S.N. Actions 1 Maintain all VSFS and other feeding sites. 2 Advocate on the effi cient regulatory mechanism to ban other NSAIDs shown to vulture-toxic. 3 Expand VSZ initiatives into the eastern lowlands. 4 Proper management of carcass dumps. 5 Advocate to provide dead livestock caracass for vultures. 6 Management of wild animal carcasses in protected and non-protected areas 6.2.5 Habitat Conservation and Safeguarding from Power Infrastructures Rationale Among six resident vultures, EV, BV and HG habitually breed in the cliff, WRV, SBV, and RHV breed on tree. In Nepal, various natures of developmental activities are being undertaken as a result the natural habitat is severely disturbed and is forced to shift from their historic habitation to other best alternate locations. Road construction, mine excavation, tree felling, river exploitation, forest fi re and other development activities nearby vulture colony are the major threats to vulture which has a direct impact on long-term survival so this issue should be seriously considered in future conservation endeavors. Electrocution and collision in power infrastructures has been one of the major threats globally to large birds of prey including vultures. Infrastructure growth in the power energy sector has been growing rapidly. Electrocution occurs when the bird is in contact with a live wire. The issue, therefore, needs to be addressed with proper guidelines, effective planning, design, and mitigation measures. Outputs 1. Natural habitat of vultures maintained and restored. 2. Sensitivity maps developed to reduce electrocution. S.N. Actions 1 Prepare and implement site-specifi c management plans in identifi ed priority areas. 2 Update information on previously known, current, and potential habitats. 3 Control cutting of the nesting and potential trees in their nesting habitat 4 Encourage and support local communities to manage and protect the habitat. VULTURE CONSERVATION ACTION PLAN (2023-2027)24 5 The awareness campaign, Sensitize and aware local forest user groups and other stakeholders 6 Protect the nesting site from all the possible disturbances 7 Information collection on the distribution of power lines in vulture habitat. 8 Sensitivity mapping of threatened vultures against hydropower and transmission lines 9 Employ mitigation measures to prevent electrocution and collision in areas where it occurs. 6.2.6 Sensitize Stakeholders and Build their Capacity Rationale Though the negative perception of vulture has changed to positive in most places still people have a negative attitude towards vultures and still do not know about the ecosystem services vulture provides. Many Vets/Para vets and local vet practitioners who use NSAIDs are still unaware of the problem caused to the vulture. Outputs 1. All conservation stakeholders are sensitized to vulture conservation. 2. Vulture conservation issue integrated into the site specifi c management plan. S.N. Actions 1 Continue to raise awareness of the diclofenac and other NSAIDs-problem. 2 Continue to raise awareness of vultures and the ecosystem service they provide. 3 Advocacy to Government Offi cial/ Organization (Local Government, DFO, Animal and Livestock Institutions, National Park Staff, Transboundary) 4 Generating Citizen Scientist. 5 Establish Vulture Stewardship initiative at important nesting sites in the western and eastern lowlands. 6 Establish information centers at all VSFS, other feeding sites, and Vulture Stewardship Sites. Stakeholder Interaction in Kawasoti, Nawalparasi VULTURE CONSERVATION ACTION PLAN (2023-2027) 25 7 Advocate the integration of vulture conservation into community forest management. 8 Provide necessary knowledge, skills, and materials for vulture conservation to individuals and communities contributing to vulture conservation. 9 Recognize and reward communities and individuals for their effort in vulture conservation. 10 Outreach Material production and distribution 6.2.7 Build Partnership at Local, National, and International Level Rationale Since the vulture fl y between India and Nepal and also some part of the VSZ lies in India, transboundary partnership is needed. Vulture conservation is largely funded by INGOs which may not be sustainable for a long run. Outputs 1. The partnership among local, national and international organization was maintained. S.N. Actions 1 Secure 5% of the government budget for vulture conservation. 2 Maintain good relationships with INGOs that provide funds and/or expertise through meeting objectives and timely reporting. 3 Partner with national, regional, and/or international organisations to secure big funds 4 Transboundary collaboration especially with Indian partners working within 100km from Vulture Safe Zone in Nepal. 5 Participate in national, regional, and international meetings and workshops to build networks and expertise. 6.2.8 Strengthen the Vulture Safe Zone Rationale Vulture Safe Zone initiatives were pioneered in Nepal developed from the ‘Diclofenac-free Zone’ Concept. Validating the VSZ which covers a 100km radius from the vulture release site and eight IBAs are lie within it. VSZ will achieve through regular monitoring of diclofenac and other toxic NSAIDs, good survival rate of the tagged vultures, ensuring a safe food supply, regular monitoring of breeding colony, awareness, empowering the community to monitor and develop a sustainable model of Vulture Safe Feeding Sites (VSFS). Nepal is now leading on the release of captive vultures which are fi tted with telemetry tags along with some wild birds and they need to be monitor effectively to verify and expaned the VSZ area and its assessment. Community engagement and strengthening their capacity in managing VSZ are highly essential for the success and effi ciency of the release programme. Since our VSZ overlaps with the territory of the neighboring country, transboundary collaboration is equally useful. Furthermore, support the local communities in capacity enhancement in monitoring and tourism promotion. Output 1. Strengthening of World's fi rst scientifi cally validated Vulture Safe Zone. S.N. Actions 1 Develop transboundary cooperative with organisations in India to extend VSZ conservation actions. 2 Partner with communities, vet professionals, Government agencies, and other conservation organisations for sustainability of VSZ 3 Monitoring NSAIDs use and effectiveness of ban of harmful NSAIDs around the Gandaki Lumbini VSZ and other proposed VSZ 4 Community managed Vulture safe feeding sites and safe carcass disposal sites 5 Awareness, sensitization, and advocacy around VSZ 6 Strengthen communities for vulture safe zone management 7 Tagged vulture movement monitoring and its assessment for foraging and breeding site. 8 Monitoring the survival of all tagged birds and identify the causes for any mortalities 9 VSZ initiative expanded into the pVSZ and to eastern lowlands VULTURE CONSERVATION ACTION PLAN (2023-2027)26 Plan Implementation and Monitoring CHAPTER: 7 7.1 Implementing Agency DNPWC takes a lead role in coordinating the overall implementation of the VCAP starting with organizing the Nepal Vulture Recovery Committee (NVRC) meeting regularly. NVRC has been formed to facilitate the smooth implementation of VCAP and foster the regional and global collaboration in saving the Asian vultures. NVRC is comprised of twelve members: 1. Chairperson- Director General, DNPWC 2. Member-Deputy Director General, DNPWC 3. Member-Deputy Director General, DoFSC 4. Member-Deputy Director General, DoA 5. Member-Deputy Director General, DLS 6. Member- Deputy Director General, DDA 7. Member- Country Representative, IUCN-Nepal 8. Member- Country Representative, ZSL Nepal 9. Member- Country Representative, WWF Nepal 10. Member- Director, NTNC 11. Member- Chief Executive Offi cer, BCN 12. Member Secretary- Under Secretary, DNPWC The key role of DNPWC is to support, facilitate and identify priority research, conservation, recovery, and monitoring projects and seek fi nancial and technical support for the implementation and work as mentioned in the NVRC. DoFSC supports the VSFS, protection, and afforestation of vulture nesting trees and awareness raising and play role in supporting the national vulture recovery committee. DDA play a key role to regulate the ban of the diclofenac and facilitate the use of alternative NSAIDs, regulate the import/illegal use and or ban of non-tested NSAIDs and support the enforcement of the ban on diclofenac and other toxic NSAIDs for veterinary use and help promote alternative safe NSAIDs (including meloxicam and tolfenamic acid) in Nepal. Department of Livestock Service will help enhance the capacity of technical manpower all over the country including the vulture habitat and legal authority they possess, awareness of para veterinarians, investigation of the causes of mass mortality, preparedness plan of diseased like Avian Infl uenza, regulate the use of human multi vial doses of diclofenac use in livestock, and facilitate and coordinate with District Livestock Service Offi ces to support and monitor the carcass sample collection to conduct NSAID test. Department of Agriculture plays the key role to monitor the use of agrochemicals impacting the vultures and raise awareness among the farmers to be part of the ecosystem management and conservation activities. DoFSC will support the implementation through the relevant agency of the state government i.e. Ministry of Industry, Tourism, Forest, and Environment. Local government (Metropolitan City, Sub- metropolitan City, Municipality, and Rural Municipality) can consolidate the role of the line agencies, NGOs, and civil society to strengthen the vulture conservation. Research Institutions and Academia collaborate with the NVRC for conducting and disseminating research and monitoring related to vulture conservation, status and recovery of vultures, and other areas prescribed in this plan. Civil society and the private sector help to disseminate information on the conservation of vultures and cross-check if veterinary practitioners are using diclofenac and other dangerous drugs for vultures in their areas, protect nesting colonies of vultures. At the regional level, Regional Steering Committee (RSC) and Saving Asia’s Vultures from Extinction (SAVE) will provide policy and technical advisory roles. International organizations such as RSPB, ZSL, SAVE will contribute technical and fi nancial support. At the central level, NVRC will provide technical advisory roles, policy guidance, and coordination. At the mid-level, a vulture conservation core team will be formed to provide technical assistance VULTURE CONSERVATION ACTION PLAN (2023-2027) 27 to implement VCAP. BCN and NTNC will support DNPWC for vulture conservation initiatives. At the local level, Project Implementation Committee will be formed as per need to ensure effective management and implementation of the specifi c project. 7.2 Financial Plan The total estimated cost for the implementation of the action plan is NPR 148,005,000. The fund will be allocated from the government’s regular budget and existing conservation partners such as RSPB, NTNC, IUCN Nepal, ZSL, WWF Nepal. Other national and international conservation organizations including local and provincial governments will be encouraged to generate additional funds for the implementation. Detail breakdown of the budget is presented in Appendix-4. The summary of the indicative budget is given below. Objectives Budget (NRP) Objective 1: Prevention of NSAIDs poisoning and control the deliberate poisoning of cattle carcass 21350000 Objective 2: Promote Scientifi c Research to Enhance Knowledge 39000000 Objective 3: Release of captive vultures into the safe environment 27450000 Objective 4: Promote safe food supply to vultures 8400000 Objective 5: Habitat Conservation and safeguarding from power infrastructure 11300000 Objective 6: Sensitize Stakeholders and Build their Capacity 12050000 Objective 7: Build Partnership at Local, National, and International Level 5250000 Objective 8: Strengthen the Vulture Safe Zone (VSZ) 8250000 Monitoring, Mid-term and fi nal review 1000000 Additional activities 500000 Administrative Cost 13455000 Total 148005000 7.3 Monitoring and Review of the Plan Implementation DNPWC, DoFSC, PA managers, DFOs, provincial governments, local government will implement and monitor the plan. A mid-term review will be conducted during the third year of the implementation and a Final review and update of the plan will be done during the 5th year of implementation which will be conducted by a team of independent consultants and will be shared during the review meetings. Slender-billed Vulture, Photo: Ankit Bilash Joshi VULTURE CONSERVATION ACTION PLAN (2023-2027)28 References Ministry of Forest and Soil Conservation. (2014). Nepal National Biodiversity Strategy and Action Plan 2014– 2020. Government of Nepal Kathmandu. Anderson, M. D., & Mundy, P. J. (2001). The demise of vultures in southern Asia: mortality factors and a risk to African vultures?: news & views. South African Journal of Science, 97(9), 342–344. Baral, H. S., & Regmi, U. R. (2012). Status and Conservation of Birds in Nepal. January, 1–30. Bhusal, K. P. (2018). Vulture Safe Zone: a landscape level approach to save the threatened vultures in Nepal. The Himalayan Naturalist, 1(1), 25–26. Bhusal, K. P., Chaudhary, I. P., & Rana, D. B. (2020). Vultures and People: Some Insights into an Ancient Relationship and Practice of Sky Burial Persisting in Trans-Himalayan Region of Nepal. Vulture Bulletin, 9(Annual Newsletter), 43–45. Bowden, C. (2017). Asian vulture crisis: Some positive signs. BirdingASIA, 27, 94–95. Bowden, C. G. R., Prakash, V., Ranade, S., Routh, A., Jakatt, R. D., Cuthbert, R., Rahmani, A. R., Green, R. E., Prakash, N., & Parry-Jones, J. (2012). Conservation breeding for the future release of the critically endangered Asian Gyps vulturesprogress of the programme in south Asia and why it is so important. J. Bombay Nat. Hist. Soc, 109, 43–45. Brown, C. J., & Plug, I. (1990). Food choice and diet of the Bearded Vulture Gypaetus barbatus in southern Africa. African Zoology, 25(3), 169–177. Brown, L., & Amadon, D. (1968). Eagles, hawks and falcons of the world. Buechley, E. R., & Sekercioglu, C. H. (2016). Vultures. Current Biology, 26(13), R560–R561. Chaudhary, A., Subedi, T. R., Giri, J. B., Baral, H. S., Bidari, B., Subedi, H. E. M., Chaudhary, B., Chaudhary, I., Paudel, K., & Cuthbert, R. J. (2012). Population trends of Critically Endangered Gyps vultures in the lowlands of Nepal. Bird Conservation International, 22(3), 270–278. Chomba, C., & M’Simuko, E. (2013). Nesting patterns of raptors; White backed vulture (Gyps africanus) and African fi sh eagle (Haliaeetus vocifer), in Lochinvar National Park on the kafue fl ats, Zambia. Open Journal of Ecology, 3(5), 325. Christie, D. A., & Ferguson-Lees, J. (2010). Raptors of the world. Bloomsbury Publishing. DNPWC/MoFE/GoN. (2009). Vulture Conservation Action Plan for Nepal (2009-2013). DNPWC. (2015). Vulture Conservation Action Plan for Nepal (2015-2019). Department of National Parks and Wildlife Conservation, Ministry of Forest and Soil Conservation, Government of Nepal, Kathmandu. Donázar, J. A., Hiraldo, F., & Bustamante, J. (1993). Factors infl uencing nest site selection, breeding density and breeding success in the bearded vulture (Gypaetus barbatus). Journal of Applied Ecology, 504–514. Eldar, R. (2008). Tibetan sky burial in China Tibetan sky burial. Etheridge, B., Summers, R. W., & Green, R. E. (1997). The effects of illegal killing and destruction of nests by humans on the population dynamics of the hen harrier Circus cyaneus in Scotland. Journal of Applied Ecology, 1081–1105. Fourie, T., Cromarty, D., Duncan, N., Wolter, K., & Naidoo, V. (2015). The safety and pharmacokinetics of carprofen, fl unixin and phenylbutazone in the Cape Vulture (Gyps coprotheres) following oral exposure. PloS One, 10(10), e0141419. VULTURE CONSERVATION ACTION PLAN (2023-2027) 29 Galligan, T. H., Bhusal, K. P., Paudel, K., Chapagain, D., Joshi, A. B., Chaudhary, I. P., Chaudhary, A., Baral, H. S., Cuthbert, R. J., & Green, R. E. (2020). Partial recovery of Critically Endangered Gyps vulture populations in Nepal. Bird Conservation International, 30(1), 87–102. Harris, R. J. (2013). The conservation of Accipitridae vultures of Nepal: a review. Journal of Threatened Taxa, 5(2), 3603–3619. Inskipp, C., Phuyal, S., Bhatta, T. R., Khatiwada, M., Inskipp, T., Gurung, S., Singh, P. B., Murray, L., Poudyal, L., & Amin, R. (2016). The status of Nepal ’s birds: the national red list series (Vol. 1). https://doi.org/10.1111/ cobi.12574 Kanaujia, A., & Kushwaha, S. (2014). Relationship between Water Bodies and Vulture Populations in Bundelkhand, India. Species, 11(27), 6–19. Ligon, J. D. (1967). Relationships of the cathartid vultures. Margalida, A., Colomer, M. A. À., & Oro, D. (2014). Man-induced activities modify demographic parameters in a long-lived species: effects of poisoning and health policies. Ecological Applications, 24(3), 436–444. Margalida, A., Heredia, R., Razin, M., & Hernández, M. (2008). Sources of variation in mortality of the Bearded Vulture Gypaetus barbatus in Europe. Bird Conservation International, 18(1), 1–10. Martínez-Haro, M., Mateo, R., Guitart, R., Soler-Rodríguez, F., Pérez-López, M., María-Mojica, P., & García Fernández, A. J. (2008). Relationship of the toxicity of pesticide formulations and their commercial restrictions with the frequency of animal poisonings. Ecotoxicology and Environmental Safety, 69(3), 396–402. Naoroji, R., & Sangha, H. S. (2006). Arunachal Pradesh, India: an ornithological diary from December 2005. Indian Birds, 2(5), 120–131. Oaks, J. L., Gilbert, M., Virani, M. Z., Watson, R. T., Meteyer, C. U., Rideout, B. A., Shivaprasad, H. L., Ahmed, S., Chaudhry, M. J. I., & Arshad, M. (2004). letters to nature-Diclofenac residues as the cause of vulture population decline in Pakistan. Nature, 427(6975), 630–632. Ogada, D., Shaw, P., Beyers, R. L., Buij, R., Murn, C., Thiollay, J. M., Beale, C. M., Holdo, R. M., Pomeroy, D., & Baker, N. (2016). Another continental vulture crisis: Africa’s vultures collapsing toward extinction. Conservation Letters, 9(2), 89–97. Pain, D. J., Cunningham, A. A., Donald, P. F., Duckworth, J. W., Houston, D. C., Katzner, T., Parry-Jones, J., Poole, C., Prakash, V., & Round, P. (2003). Causes and effects of temporospatial declines of Gyps vultures in Asia. Conservation Biology, 17(3), 661–671. Paudel, K. (2013). Community-based Ecological monitoring of critically endangered Oriental White-backed Vultures in Suklaphanta Wildlife Reserve, Important Bird Area, Nepal. Prakash, V., Pain, D. J., Cunningham, A. A., Donald, P. F., Prakash, N., Verma, A., Gargi, R., Sivakumar, S., & Rahmani, A. R. (2003). Catastrophic collapse of Indian white-backed Gyps bengalensis and long-billed Gyps indicus vulture populations. Biological Conservation, 109(3), 381–390. Rana, D. B., Chaudhary, I. P., Joshi, H. L. D. A. B., & Bhusal, K. P. (2019). Monitoring of Nest and Breeding Status of White-rumped Vulture Gyps bengalensis in Nepal. Vulture Bulletin, 8(Annual Newsletter), 28–31. Selva, N., & Fortuna, M. A. (2007). The nested structure of a scavenger community. Proceedings of the Royal Society B: Biological Sciences, 274(1613), 1101–1108. Subedi TR, Pe ́rez-Garcı ́a JM, Sah SAM, Gurung S, Baral HS, Poudyal LP, et al. Spatial and temporalmovement of the bearded vulture using GPS telemetry in the Himalayas of Nepal. Ibis. 2020; 162(2):563–71. https:// doi.org/10.1111/ibi.1279946 Yadav Ruby, A. K., & Kanaujia, A. (2018). A Review on Aerial Display, Nest site selection, Nest Defense, Courtship display, Copulation, Parental care: key events of vultures during Breeding, threats and Management. International Journal of Life Sciences, 6(2), 586–604. VULTURE CONSERVATION ACTION PLAN (2023-2027)30 Appendix 1: Species Fact Sheet English Name White-rumped Vulture Nepali Name 8ª\u/ lu4 Scientifi c Name Gyps bengalensis Species Attribute Resident Altitude Upper limit: 1800 m (-3100 m); lower limit: 75 m Distribution in Nepal Arghakhachi, Banke, Bardiya, Chitwan, Dang, Gorkha, Kailali, Kanchanpur, Kapilvastu, Kaski, Nawalparasi, Palpa, Pyuthan, Rupandehi, Saptari, Sarlahi, Sunsari, Syangja, Tanahu, Udyapur Distribution in Protected area Annapurna Conservation Area, Chitwan National Park, Banke National Park Bardiya National Park, , Koshi-tappu Wildlife Reserve, Shuklaphanta National Park, Parsa National Park Global Distribution Afghanisthan, Bangladesh, Bhutan, Brunei, China (Mainland), India, Iraq, Iran, Laos, Malysia, Myanmar, Nepal, Pakistan, Russia, Thailand, Vietnam National Status Critically Endangered Global Status Critically Endangered National Population Status <2000 Global Population Estimation 2500-9999 estimated Threats Disturbance, direct and secondary poisoning, electrocution and collision in powerlines, reduced food availability and habitat change, road Construction, mine exploration, land excavation, use of vulture toxic NSAIDs VULTURE CONSERVATION ACTION PLAN (2023-2027) 31 English Name Slender-billed Vulture Nepali Name ;fgf] v}/f] lu4 Scientifi c Name Gpys tenuirostris Species Attribute Resident Altitude Upper limit: 1800 m (-3100 m); lower limit: 75 m Distribution in Nepal Arghakhachi, Dang, Kailali, Kanchanpur, Kapilvastu, Kaski, Nawalparasi, Palpa, Rupandehi, Sarlahi, Syangja, Tanahu Distribution in Protected area Chitwan National Park, Shuklaphanta National Park Global Distribution Bangladesh, Cambodia, India, Laos, Malaysia, Myanmar, Nepal, Thailand, Vietnam National Status Critically Endangered Global Status Critically Endangered National Population Status 50-75 Global Population Estimation 1000-2499 estimated Threats Intentional or unintentional effects-persecution/control, poisoning, electrocution and collision in powerlines, reduced food availability and habitat change, use of vulture toxic NSAIDs VULTURE CONSERVATION ACTION PLAN (2023-2027)32 English Name Red-headed Vulture Nepali Name ;'g lu4 Scientifi c Name Sarcogyps calvus Species Attribute Resident Altitude Upper limit: 2000 m (-3050 m); lower limit: 75 m Distribution in Nepal Aacham, Arghakhachi, Bajura, Chitwan, Dadeldhura, Dailekh, Dang, Darchula, Doti, Gorkha, Gulmi, Jajarkot, Kailali, Kalikot, Kanchanpur, Kapilvastu, Kaski, Lalitpur, Myagdi, Nawalparasi, Palpa, Parbat, Pyuthan, Rolpa, Rupandehi, Salyan, Syangja, Tanahu Distribution in Protected area Annapurna Conservation Area, Banke National Park, Chitwan National Park, Shuklaphanta National Park, Shivapuri-Nagarjun National Park, Shuklaphanta National Park Global Distribution Bangladesh, Bhutan, Cambodia, China, India, Laos, Malaysia, Myanmar, Nepal, Pakistan, Thailand, Vietnam National Status Critically Endangered Global Status Critically Endangered National Population Status 200-400 Global Population Estimation 2500-9999 estimated Threats Disturbance, lead poisoning (from ammunition used in hunting game), direct and secondary poisoning, electrocution and collision in powerlines, reduced food availability and habitat change, use of vulture toxic NSAIDs VULTURE CONSERVATION ACTION PLAN (2023-2027) 33 English Name Egyptian Vulture Nepali Name ;]tf] lu4, uf]a|] lu4 Scientifi c Name Neophron percnopterus Species Attribute Resident Altitude Upper limit: 2900 m (-3810 m); lower limit: 75 m Distribution in Nepal Arghakhachi, Baglung, Bajura, Banke, Dailekh, Dang, Darchula, Dhadhing, Gorkha, Gulmi, Jajarkot, Kanchanpur, Kapilvastu, Kaski, Myagdi, Nawalparasi, Nuwakot, Palpa, Parbat, Pyuthan, Ramechhap, Rolpa, Rukum, Rupandehi, Salyan, Syangja, Tanahu Distribution in Protected area Annapurna Conservation Area, Chitwan National Park, Rara National Park, Dhorpatan Hunting Reserve, Bardiya National Park, Shuklaphanta National Park, Shivapuri Nagarjun National Park, Parsa National Park, Langtang National Park, Api Nampa National Park, Banke National Park Global Distribution Afghanisthan, Albania, Algeria, Andorra, Angola, Armenia, Austria, Azerbaijan, Bangladesh, Belgium, Benin, Bosnia and Herzegovina, Botswana, Bulgaria, Burkina Faso, Cameroon, Cape Verde, Central African Republic, Chad, China (Mainland), Congo, Croatia, Cyprus, Czechila, Denmark, Djibouti, Egypt, Eritrea, Estonia, Ethiopia, Finland, France, Fambia, Georgia, Ghana, Gibraltar, , Greece, Guinea-Bissau, Hungary, India, Iran, Iraq, Israel, Italy, Jordan, Kazakhastan, Kenya, Kuwait, Kyrgyzstan, Lebanon, Lesotho, Libya, Mali, Malta, Mauritania, Moldova, Mongolia, Montenegro, Morocco, Mozambique, Myanmar, Namibia, Nepal, Niger, Nigeria, North Macedonia, Norway, Oman, Pakistan, Palestine, Poland, Portugal, Quatar, Romania, Russia, Saudi Arabia, Senegal, Serbia, Slovakia, Slovenia, Somalia, South Africa, South Sudan, Spain, Sri Lanka, Sudan, Sweden, Switzerland, Syria, Tajkistan, Tanzania, Togo, Tunisia, Turkey, Turkmenistan, Uganda, Ukraine, United Arab Emirates, United Kingdom, Uzbekistan, Western Sahara, Yamen, Zimbabwe National Status Vulnerable Global Status Endangered National Population Status 300-1000 Global Population Estimation 12000-38000 estimated Threats Disturbance, direct and secondary poisoning, electrocution and collision in powerlines, reduced food availability and habitat change, use of vulture toxic NSAIDs VULTURE CONSERVATION ACTION PLAN (2023-2027)34 English Name Bearded Vulture Nepali Name xf8kmf]/ lu4 Scientifi c Name Gypaetus barbatus Altitude Upper limit: 5600 m (-7500 m); lower limit: 250 m Distribution in Nepal Arghakhachi, Baglung, , Baitadi, Bajura, Dadeldhura, Dailekh, Darchula, Dolpa, Gorkha, Gulmi, Jajarkot, Kaski, Manang, Mugu, Mustang, Myagdi, Palpa, Parbat, Pyuthan, Ramechhap, Rasuwa, Rolpa, Salyan, Sankhuwasabha, Solukhambu, Syangja, Tanahu Distribution in Protected area Annapurna Conservation Area, Api Nampa National Park, Dhorpatan Hunting Reserve, Kanchanjunga Conservation Area, Langtang National Park, Makalu Barun National Park, Manaslu Conservation Area, Rara National Park, Sagarmatha National Park Global Distribution Afghanistan, Albania, Algeria, Andorra, Armenia, Austria, Azerbaijan, Bhutan, Bosnia, Bulgaria, China, Croatia, Cyprus, Czechia, Djibouti, Egypt, Eritrea, Estonia, Ethiopia, France, Georgia, Germany, Greece, India, Iran, Iraq, Israel, Italy, Jordan, Kazakhastan, Kenya, Kyrgyzstan, Lebanon, Lesotho, Liechtenstein, Mauritania, Mongolia, Montenegro, Morocco, Mozambique, Namibia, Nepal, North Korea, North Macedonia, Pakistan, Palestine, Portugal, Romania, Russia, Saudi Arabia, Serbia, Somalia, South Africa, Spain, Sudan, Switzerland, Syria, Tajkistan, Tanzania, Turkey, Turkmenistan, Uganda, Uzbekistan, Yamen, Zimbabwe National Status Vulnerable Global Status Near Threatened National Population Status <500 Global Population Estimation 1300-6700 estimated Threats Direct persecution, habitat degradation, disturbance of breeding birds, inadequate food availability use of vulture toxic NSAIDs VULTURE CONSERVATION ACTION PLAN (2023-2027) 35 English Name Himalayan Griffon Nepali Name lxdfnL lu4 Scientifi c Name Gyps himalayensis Species Attribute Resident Altitude Upper limit: 6100 m; lower limit: 75 m Distribution in Nepal Aacham, Arghakhachi, Baglung, Baitadi, Bajhang, Bajura, Banke, Bardiya, Bhaktapur, Chitwan, Dadeldhura, Dailekh, Darchula, Dadhing, Dhankuta, Dhanusa, Dolpa, Doti, Gorkha, Gulmi, Humla, Jajarkot, Jhapa, Jumla, Kalikot, Kailali, Kanchanpur, Kapilvastu, Kaski, Kathmandu, Lalitpur, Lamjung, Manang, Mugu, Mustang, Myagdi, Nawalparasi, Nuwakot, Okhaldhunga, Palpa, Parbat, Pyuthan, Ramechhap, Rasuwa, Rautahat, Rolpa, Rukum, Rupandehi, Salyan, Sankhuwasabha, Saptari, Sarlahi, Sindhupalchowk, Siraha, Solukhumbu, Sunsari, Surkhet, Syangja, Tanahu, Taplejung, Udyapur Distribution in Protected area Annapurna Conservation Area, Chitwan National Park, Rara National Park, Dhorpatan Hunting Reserve, Bardiya National Park, Shuklaphanta National Park, Shivapuri-Nagarjun National Park, Parsa National Park, Langtang National Park, Api Nampa National Park, Banke National Park, Koshi-Tappu Wildlife Reserve, Manaslu Conservation Area, Gaurisankhar Conservation Area, Makalu-Barun National Park, Sagarmatha National Park, Kanchanjunja Conservation Area Global Distribution Afghanistan, Bangladesh, Bhutan, Cambodia, China (mainland), India, Kazakhstan, Kyrgyzstan, Malaysia, Mongolia, Myanmar, Nepal, Pakistan, Singapore, Tajikistan, Thailand, United Arab Emirates, Uzbekistan National Status Vulnerable Global Status Near Threatened National Population Status <10000 Global Population Estimation 66000-334000 estimated Threats Disturbance, direct and secondary poisoning, electrocution and collision in powerlines, mining, reduced food availabilty and habitat change, use of vulture toxic NSAIDs VULTURE CONSERVATION ACTION PLAN (2023-2027)36 English Name Indian Vulture Nepali Name nfdf]7"“8] lu4 Scientifi c Name Gyps indicus Species Attribute Vagrant Altitude Upper limit:800m, lower limit:75 m Distribution in Nepal Nawalpur, Kapilvastu, Pokhara Distribution in Protected area Chitwan National Park Global Distribution Afghanistan, India, Nepal Pakistan National Status Critically Endangered Global Status Critically Endangered National Population Status Global Population Estimation 30000 estimated Threats Disturbance, direct and secondary poisoning, electrocution and collision in powerlines, reduced food availability and habitat change, use of vulture toxic NSAIDs VULTURE CONSERVATION ACTION PLAN (2023-2027) 37 English Name Griffon Vulture Nepali Name v}/f] lu4 Scientifi c Name Gyps fulvus Species Attribute Passage Migrant Altitude Upper limit: uncertain, at least 2000 m; lower limit:75 m Distribution in Nepal Baitadi, Bajura, Kanchanpur, Kapilvastu, Kaski, Myagdi, Nawalparasi, Ramechhap, Rupandehi, Sunsari Distribution in Protected area Annapurna Conservation Area, Chitwan National Park, Rara National Park, Shuklaphanta National Park Global Distribution Afghanistan, Albania, Algeria, Armenia, Austria, Azerbaijan, Bangladesh, Belarus, Belgium, Bhutan, Bosnia and Bulgaria, China (Mainland), Croatia, Cyprus, Czechila, Denmark, Djibouti, Egypt, Eritrea, Estonia, Ethiopia, Finland, France, Georgia, Gibraltar (to UK), , Greece, Hungary, India, Iran, Iraq, Israel, Italy, Jordan, Kazakhstan, Kenya, Kuwait, Kyrgyzstan, Latvia, Lebanon, Mali, Malta, Mauritania, Mongolia, Montenegro, Morocco, Nepal, Netherlands, Niger, North Macedonia, Oman, Pakistan, Palestine, Poland, Portugal, Romania, Russia, Saudi Arabia, Senegal, Serbia, Slovakia, Slovenia, Somalia, Spain, Sudan, Switzerland, Syria, Tajkistan, Togo, Tunisia, Turkey, Turkmenistan, Ukraine, United Arab Emirates, Uzbekistan, Western Sahara, Yamen National Status Least Concerned Global Status Least Concerned National Population Status Global Population Estimation 500000-999999 estimated Threats Disturbance, lead poisoning (from ammunition used in hunting game), direct and secondary poisoning, electrocution and collision in powerlines, collisions with wind turbines, reduced food availability and habitat change, use of vulture toxic NSAIDs VULTURE CONSERVATION ACTION PLAN (2023-2027)38 English Name Cinereous Vulture Nepali Name /fh lu4 Scientifi c Name Aegypius monachus Species Attribute Passage Migrant Altitude Upper limit: 2900 m (-3810 m); lower limit: 75 m Distribution in Nepal Arghakhachi Baglung, Baitadi, Bardiya, Chitwan, Dailekh, Dang, Gorkha, Jajarkot, Kailali, Kanchanpur, Kapilvastu, Kaski, Lalitpur, Manang, Mustang, Morang, Myagdi, Nawalparasi, Palpa, Parbat, Ramechhap, Rupandehi, Saptari, Syangja, Tanahu Distribution in Protected area Annapurna Conservation Area, Chitwan National Park, Banke National Park, Rara National Park, Dhorpatan Hunting Reserve, Bardiya National Park, Shuklaphanta National Park, Shivapuri-Nagarjun National Park Global Distribution Afghanisthan, Albania, Armenia, Austria, Azerbaijan, Bangladesh, Belgium, Benin, Bosnia and Herzegovina, Botswana, Belerus, Bhutan, Bosnia, Bulgaria, Cambodia, China (Mainland), Croatia, Cyprus, Czechila, Egypt, France, Georgia, Germany, Gibraltar (to UK), Greece, Hungary, India, Iran, Iraq, Israel, Italy, Japan, Jordan, Kazakhastan, Latvia, , Lebanon, Malyasia, Moldova, Mongolia, Montenegro, Morocco, Myanmar, Nepal, Netherland, North Korea, North Macedonia, Oman, Pakistan, Poland, Portugal, Romania, Russia, Saudi Arabia, Serbia, Slovakia, Slovenia, South Korea, Spain, Sudan, Switzerland, Syria, Taiwan, Tajkistan, Thailand, Tunisia, Turkey, Turkmenistan, Ukraine, Uzbekistan, Vietnam, Yemen National Status Endangered Global Status Near Threatened National Population Status 60-100 Global Population Estimation 15600-21000 estimated Threats Disturbance, lead poisoning (from ammunition used in hunting game), direct and secondary poisoning, electrocution and collision in powerlines, collisions with wind turbines, reduced food availability and habitat change, use of vulture toxic NSAIDs VULTURE CONSERVATION ACTION PLAN (2023-2027) 39 Ap pe nd ix 2 : L og ic al Fr am ew or k Hi er ar ch y of O bj ec tiv es Ob je ct iv el y Ve rifi a bl e In di ca to rs M ea ns o f V er ifi ca tio n Ri sk s/ As su m pt io ns Go al : R es to re a nd m ai nt ai n vi ab le w ild p op ul at io ns in N ep al Ob je ct iv e: E ns ur e vi ab le w ild po pu la tio ns o f a ll th e sp ec ie s of vu ltu re s th ro ug h pr ov is io n of s af e fo od a nd m ai nt en an ce o f s ui ta bl e ha bi ta t. · Al l s pe ci es o f v ul tu re ’s po pu la tio n an d ne st in g si te s in cr ea se d. · No v ul tu re d ie s fro m N SA ID a nd p oi so ni ng . · Sc ie nt ifi ca lly p ro ve n VS Zs Vu ltu re p op ul at io n su rv ey re po rt Vu ltu re P os t m or te m re po rt Sa te lli te ta gg ed v ul tu re re po rt SA VE re po r Ob je ct iv e 1: Pr ev en tio n of N SA ID s po is on in g an d co nt ro l t he d el ib er at e po is on in g of c at tle c ar ca ss Ou tp ut 1.1 Ba n on v ul tu re to xi c NS AI Ds lik e Ac ce cl of en ac , K et op ro fe n, Ni m es ul id e an d ot he r t ox ic co m po un ds . 1.2 Vu ltu re s af e NS AI Ds li ke M el ox ic am a nd To lfe na m ic a ci d av ai la bl e on m ar ke t. · An e nf or ce b an o n ve te rin ar y an d m ul ti do se o f Ac ce cl of en ac , K et op ro fe n an d Ne m us ul id e · Re gu la to ry m ec ha ni sm to b an o th er N SA ID s sh ow n to b e vu ltu re t ox ic . · En su re th e sa le o f V et er in ar y NS AI Ds o n pr es cr ip tio n an d th e tr ea tm en t o f l iv es to ck is d on e on ly u nd er th e su pe rv is io n of a q ua lifi e d ve te rin ar ia n · Se tti ng u p dr ug s af et y te st in g fa ci lit y an d sa fe ty te st n ew NS AI D m ol ec ul es o n vu ltu re s · M od al iti es e ns ur in g th e on ly a ni m al s th at d ie d wi th ou t ge tti ng a ny tr ea tm en t s ho ul d be s en t t o ca rc as s du m ps . · En su rin g th e gu id el in es fo r t he u se a nd s al e of A gr ic ul tu ra l pe st ic id es /i ns ec tic id es /h er bi ci de DD A/ DL S di re ct iv es Ph ar m ac y su rv ey re po rt Vu ltu re re le as e re po rt Vu ltu re p os t m or te m re po rt SA VE R ep or t Ob je ct iv e 2: P ro m ot e sc ie nt ifi c re se ar ch to e nh an ce k no wl ed ge Ou tp ut s 1.1 Sc ie nc e ba se d in fo rm at io n sy st em d oc um en te d. 1.2 Ce nt ra l d at ab as e on a ll vu ltu re sp ec ie s av ai la bl e. · An nu al V ul tu re p op ul at io n an d ne st in g su rv ey fo llo wi ng sa m e m et ho ds a s do ne d ur in g pr ev io us s ur ve ys . · An nu al P ha rm ac ie s su rv ey . · Id en tif yi ng th e fo ra gi ng s ite , s ur vi va l a nd c au se s of d ea th o f wi ld a nd c ap tiv e re le as ed v ul tu re s wi th te le m et ry d at a. · Ce nt ra l d at ab as e m ai nt ai ns . · Co m pi le , a na ly ze d at a an d pu bl is h re su lts in g oo d sc ie nt ifi c jo ur na l. Vu ltu re p op ul at io n an d ne st in g su rv ey re po rt Ph ar m ac ie s su rv ey re po rt Vu ltu re re le as e re po rt Ce nt ra l d at ab as e SA VE re po rt VULTURE CONSERVATION ACTION PLAN (2023-2027)40 Ob je ct iv e 3: R el ea se o f C ap tiv e vu ltu re in to th e sa fe e nv iro nm en t Ou tp ut 1.1 Su cc es sf ul s ur vi va l o f c ap tiv e vu ltu re a ro un d VS Z. · Av ia ry m ai nt en an ce a nd h yg ie ne m ai nt ai n. · Ca pt iv e W RV s uc ce ss fu lly re le as ed in V SZ s. · Co nt in ue tr ac ki ng a nd m on ito rin g of th e re le as ed a nd w ild vu ltu re s wi th te le m et ry d at a. · No d ea th o f c ap tiv e re le as ed a nd w ild v ul tu re w ith a ny po is on in g. VC BC re po rt DN PW C/ CN P re po rt SA VE re po rt Ob je ct iv e 4: P ro m ot e Sa fe F oo d su pp ly to v ul tu re Ou tp ut 1.1 Av ai la bl e of S af e fo od s up pl y to vu ltu re s. · En su rin g th e gu id el in es fo r t he u se a nd s al e of A gr ic ul tu ra l pe st ic id es /i ns ec tic id es /h er bi ci de s · Da ta ba se o f a ll th e in ci de nc e of th e po is on in g. · En su re th e sa le o f V et er in ar y NS AI Ds o n pr es cr ip tio n an d th e tr ea tm en t o f l iv es to ck is d on e on ly u nd er th e su pe rv is io n of a q ua lifi e d ve te rin ar ia n DD A/ DL S di re ct iv es Ph ar m ac y su rv ey re po rt Vu ltu re re le as e re po rt SA VE re po rt Ob je ct iv e 5: H ab ita t C on se rv at io n an d sa fe gu ar di ng fr om p ow er in fra st ru ct ur es Ou tp ut s 1.1 Na tu ra l H ab ita t o f v ul tu re s m ai nt ai ne d an d re st or ed . 1.2 Se ns iti vi ty m ap s de ve lo pe d to re du ce e le ct ro cu tio n. M or e si gh tin gs o f v ul tu re ’s/ v ul tu re p op ul at io n in cr ea se d M or e ne st in g si te re co rd ed . Si te s pe ci fi c m an ag em en t p la n de ve lo pe d. Se ns iti vi ty m ap pi ng d ev el op ed M iti ga tio n m ea su re s to re pl ac e th e ex is tin g el ec tr ic p ol es w ith in su la to rs a nd b ird fr ie nd ly p ol es Su rv ey re po rt Sc ie nt ifi c ar tic le M an ag em en t p la n M ed ia a rt ic le s Ob je ct iv e 6: S en si tiz e st ak eh ol de rs a nd b ui ld th ei r c ap ac ity Ou tp ut s 1.1 Al l c on se rv at io n st ak eh ol de rs se ns iti ze d on v ul tu re co ns er va tio n. 1.2 Vu ltu re c on se rv at io n is su e in te gr at ed in s ite s pe ci fi c m an ag em en t p la n. · St ak eh ol de rs in iti at e m on ito rin g an d ha bi ta t c on se rv at io n · Al l p ro te ct ed A re as , b uf fe rz on es , c om m un ity fo re st an d ot he r c on se rv at io n ag en ci es m ai ns tr ea m v ul tu re co ns er va tio n in th ei r r es pe ct iv e m an ag em en t/ wo rk p la ns M an ag em en t / wo rk p la ns M ed ia a rt ic le s Re se ar ch re po rt s VULTURE CONSERVATION ACTION PLAN (2023-2027) 41 Ob je ct iv e 7: Bu ild P ar tn er sh ip a t l oc al , n at io na l a nd in te rn at io na l l ev el Ou tp ut s 1.1 Pa rt ne rs hi p am on g na tio na l an d in te rn at io na l o rg an iza tio n m ai nt ai ne d. · Go ve rn m en t c on tr ib ut io n on v ul tu re c on se rv at io n · Re gu la r f un di ng s up po rt fr om th e pa rt ne r o rg an iza tio n bo th na tio na lly a nd in te rn at io na lly . An nu al re po rt Go ve rn m en t r ep or ts M oU s/ c on tra ct s Pa rt ne rs re po rt SA VE R ep or t Ob je ct iv e 8: S tr en gt he n th e vu ltu re s af e zo ne Ou tp ut 1.1 St re ng th en in g of W or ld 's fi r st sc ie nt ifi ca lly v al id at ed V ul tu re Sa fe Z on e. · Fi nd in gs o f s ur vi va l a nd c au se s of d ea th o f w ild a nd c ap tiv e vu ltu re w ith s at el lit e ta gs in V SZ s. · Aw ar en es s an d st ro ng a dv oc ac y wi th lo ca l, st ak eh ol de rs a nd de ci si on m ak er s. · Ev al ua tin g re m ai ni ng p VS Z fo r s ci en tifi c al ly p ro ve n an d ap pr ov ed V SZ s · Vu ltu re p op ul at io n wi th in th e VS Z is s ta bl e or in cr ea si ng . · VS Z in iti at iv e ex pa nd ed in to th e ea st er n lo wl an ds Re se ar ch re po rt Sc ie nt ifi c ar tic le M ed ia a rt ic le SA VE re po rt Ap pe nd ix 3 : F iv e Ye ar B ud ge t f or V ul tu re C on se rv at io n Ac tio n Pl an S. N. Ac tiv iti es Ye ar 1 Ye ar 2 Ye ar 3 Ye ar 4 Ye ar 5 To ta l ( NP R) Ob je ct iv e 1: Pr ev en tio n of N SA ID s po is on in g an d co nt ro l t he d el ib er at e po is on in g of c at tle c ar ca ss 1.1 Ad vo ca te a b an o n Ac ce cl of en ac , K et op ro fe n an d Ne m us ul id e. 15 0, 00 0 15 0, 00 0 15 0, 00 0 15 0, 00 0 15 0, 00 0 75 0, 00 0 1.2 Ad vo ca te o n ef fi c ie nt re gu la to ry m ec ha ni sm to b an o th er NS AI Ds s ho wn to v ul tu re t ox ic a nd c ar ca ss p oi so ni ng . 20 0, 00 0 20 0, 00 0 10 0, 00 0 10 0, 00 0 20 0, 00 0 80 0, 00 0 1.3 Ef fe ct iv e m on ito rin g of im po rt a nd d is tr ib ut io n of N SA ID s / to xi c dr ug a nd m on ito rin g of d ru g pr es cr ib er s. 10 0, 00 0 10 0, 00 0 10 0, 00 0 10 0, 00 0 10 0, 00 0 50 0, 00 0 1.4 Sa fe ty te st in g of re ce nt ly in tr od uc ed o r s o ca lle d to xi c fo r vu ltu re s. 50 0, 00 0 30 0, 00 0 30 0, 00 0 30 0, 00 0 30 0, 00 0 1,7 00 ,0 00 VULTURE CONSERVATION ACTION PLAN (2023-2027)42 1.5 Re se ar ch o n An tim ic ro bi al s en si tiv ity te st to m on ito r t he an tib io tic re si st an ce in v ul tu re s an d ac ce ss th e im pa ct o n hu m an h ea lth . 50 0, 00 0 50 0, 00 0 50 0, 00 0 50 0, 00 0 50 0, 00 0 2, 50 0, 00 0 1.6 En ga ge a ge nc ie s an d or ga ni za tio ns w or ki ng in N ep al In di a bo rd er a re a to re m ov e m ul ti do se v ia ls o f d ic lo fe na c. 20 0, 00 0 20 0, 00 0 20 0, 00 0 20 0, 00 0 20 0, 00 0 1,0 00 ,0 00 1.7 Co nt in ue to ra is e aw ar en es s of th e vu ltu re t ox ic a nd v ul tu re sa fe N SA ID s an d In ci de nt al p oi so ni ng . 35 0, 00 0 25 0, 00 0 25 0, 00 0 35 0, 00 0 25 0, 00 0 1,4 50 ,0 00 1.8 En su re s al e of v et er in ar y NS AI Ds o nl y on p re sc rip tio n an d re gu la tin g th e us e of e as ily a va ila bl e of p ot en t a gr ic ul tu re pe st ic id es . 10 0, 00 0 10 0, 00 0 10 0, 00 0 10 0, 00 0 10 0, 00 0 50 0, 00 0 1.9 Pr om ot e ot he r N SA ID s pr ov en to b e vu ltu re s af e an d of g oo d qu al ity . 15 0, 00 0 15 0, 00 0 15 0, 00 0 15 0, 00 0 15 0, 00 0 75 0, 00 0 1.1 0 Co lle ct io n of d ea d vu ltu re s an d co nd uc t p os t m or te m ex am in at io n to fi nd th e ca us es o f i ts m or ta lit y. 30 0, 00 0 30 0, 00 0 30 0, 00 0 30 0, 00 0 30 0, 00 0 1,5 00 ,0 00 1.1 1 Aw ar en es s – Ve ts /P ar a ve ts a nd lo ca l v et p ra ct io ne r (R es tra in in g/ F irs t a id / Sa m pl e co lle ct io n & d is pa tc h to la bo ra to ry . 40 0, 00 0 40 0, 00 0 40 0, 00 0 40 0, 00 0 40 0, 00 0 2, 00 0, 00 0 1.1 2 Es ta bl is hm en t o f r es cu e Ce nt er a t e ac h Pr ov in ci al le ve l. 1,0 00 ,0 00 1,0 00 ,0 00 1,0 00 ,0 00 1,0 00 ,0 00 1,0 00 ,0 00 5, 00 0, 00 0 1.1 3 St re ng th en in g of la bo ra to ry fo r d ia gn os is /r es ea rc h of to xi co lo gi ca l c as es in v ul tu re s. 50 0, 00 0 50 0, 00 0 50 0, 00 0 50 0, 00 0 50 0, 00 0 2, 50 0, 00 0 1.1 4 Cr ea tin g Da ta ba se o f p oi so ni ng in ci de nc es 50 ,0 00 50 ,0 00 50 ,0 00 50 ,0 00 50 ,0 00 25 0, 00 0 1.1 5 De ve lo pm en t o f fi e ld le ve l d ia gn os tic p ro to co ls fo r e ffe ct iv e di ag no si s of h ea lth p ro bl em 10 0, 00 0 50 ,0 00 15 0, 00 0 Ob je ct iv e 2: P ro m ot e Sc ie nt ifi c Re se ar ch to E nh an ce K no wl ed ge 2.1 Re gu la r m on ito rin g of v ul tu re p op ul at io ns u si ng ro ad tr an se ct su rv ey s. 35 0, 00 0 35 0, 00 0 35 0, 00 0 35 0, 00 0 35 0, 00 0 1,7 50 ,0 00 2. 2 Re gu la r v ul tu re c ou nt a ll ov er th e co un tr y. 30 0, 00 0 30 0, 00 0 30 0, 00 0 30 0, 00 0 30 0, 00 0 1,5 00 ,0 00 VULTURE CONSERVATION ACTION PLAN (2023-2027) 43 2. 3 Ne st m on ito rin g vu ltu re p op ul at io n br ee di ng s uc ce ss . 40 0, 00 0 40 0, 00 0 40 0, 00 0 40 0, 00 0 40 0, 00 0 2, 00 0, 00 0 2. 4 M on ito r N SA ID a va ila bi lit y in v et er in ar y ph ar m ac ie s th ro ug h op en a nd u nd er co ve r s ur ve ys . 35 0, 00 0 35 0, 00 0 35 0, 00 0 35 0, 00 0 35 0, 00 0 1,7 50 ,0 00 2. 5 M on ito r N SA ID p re va le nc e in li ve st oc k an d vu ltu re c ar ca ss es . 40 0, 00 0 40 0, 00 0 40 0, 00 0 40 0, 00 0 40 0, 00 0 2, 00 0, 00 0 2. 6 Co nt in ue s at el lit e ta gg in g of a ll th e ca pt iv e re le as ed v ul tu re s. 3, 00 0, 00 0 3, 00 0, 00 0 3, 00 0, 00 0 9, 00 0, 00 0 2. 7 Ca pt ur e an d ta g th e wi ld v ul tu re s 4, 00 0, 00 0 3, 00 0, 00 0 3, 00 0, 00 0 10 ,0 00 ,0 00 2. 8 Co nt in ue m on ito rin g, tr ac ki ng a nd g ro un d tr ut hi ng o f t ag ge d vu ltu re s, re co ve r t he c or ps es a nd e st ab lis h ca us e of d ea th . 20 0, 00 0 20 0, 00 0 20 0, 00 0 20 0, 00 0 20 0, 00 0 1,0 00 ,0 00 2. 9 Ex pa nd k no wl ed ge o n vu ltu re b io lo gy a nd e co lo gy . 30 0, 00 0 40 0, 00 0 40 0, 00 0 50 0, 00 0 50 0, 00 0 2,1 00 ,0 00 2.1 0 Ex pa nd e xp er tis e in fi el d, la b an d de sk b as ed s ci en ce . 30 0, 00 0 40 0, 00 0 40 0, 00 0 50 0, 00 0 50 0, 00 0 2,1 00 ,0 00 2.1 1 As se m bl e an d m ai nt ai n a ce nt ra l d at ab as e. 40 0, 00 0 40 0, 00 0 80 0, 00 0 2.1 2 Pr od uc e re po rt s, ar tic le s an d ot he r m ed ia fo r d is se m in at io n am on g a va rie d au di en ce . 50 0, 00 0 50 0, 00 0 50 0, 00 0 50 0, 00 0 50 0, 00 0 2, 50 0, 00 0 2.1 3 En ga ge a nd s up po rt c om m un iti es in n es tin g si te a nd tr ee pr ot ec tio n. 40 0, 00 0 40 0, 00 0 40 0, 00 0 40 0, 00 0 40 0, 00 0 2, 00 0, 00 0 2.1 4 In cl ud e RH V, S BV a nd W RV in th e lis t o f p ro te ct ed b ird . 30 0, 00 0 30 0, 00 0 2.1 5 Se cu re lo ng t er m fu nd in g an d su st ai na bl e pr ac tic e fo r i n si tu ac tiv iti es . 20 0, 00 0 20 0, 00 0 Ob je ct iv e 3: R el ea se o f c ap tiv e vu ltu re in to th e sa fe e nv iro nm en t 3.1 M ai nt ai n ca pt iv e po pu la tio n in g oo d he al th . P ro du ce a s m an y fl e dg in g’ s as p os si bl e by n at ur al m et ho ds . 5, 00 0, 00 0 5, 00 0, 00 0 5, 00 0, 00 0 4, 00 0, 00 0 19 ,0 00 ,0 00 3. 2 Co nt in ue b io s ec ur ity , r eg ul ar h ea lth s cr ee ni ng a nd v et er in ar y ca re a t V CB C. 30 0, 00 0 30 0, 00 0 30 0, 00 0 30 0, 00 0 1,2 00 ,0 00 3. 3 Co nt in ue to d et er m in e th e se xe s of c ap tiv e po pu la tio n us in g ge ne tic te ch ni qu es . 50 0, 00 0 20 0, 00 0 10 0, 00 0 80 0, 00 0 VULTURE CONSERVATION ACTION PLAN (2023-2027)44 3. 4 Co ns tr uc t n ec es sa ry in fra st ru ct ur e fo r r ei nt ro du ct io ns a nd m ai nt en an ce . 10 0, 00 0 10 0, 00 0 20 0, 00 0 3. 5 Tr an sf er c ap tiv e re ar ed b ird s al on g wi th c ap tiv e br ed c hi ck s of pr ev io us y ea r t o pr e re le as e fa ci lit y. 20 0, 00 0 20 0, 00 0 20 0, 00 0 60 0, 00 0 3. 6 Co nt in ue s at el lit e ta gg in g of a ll th e ca pt iv e re le as ed v ul tu re s. 3. 7 Co nt in ue to re le as e ca pt iv e br ed v ul tu re s an d al so re le as e ot he r b ird s by m ai nt ai ni ng b es t br ee di ng b ird s an nu al ly a nd fi n al ly re le as e al l t he c ap tiv e bi rd s by 2 02 3. 20 0, 00 0 20 0, 00 0 20 0, 00 0 60 0, 00 0 3. 8 De ve lo p VC BC in to V ul tu re R es ea rc h Ce nt er . 50 0, 00 0 50 0, 00 0 1,0 00 ,0 00 3. 9 Cr ea te E m er ge nc y Fu nd fo r c ris is m an ag em en t i nc lu di ng di se as e ou tb re ak s. 1,0 00 ,0 00 1,0 00 ,0 00 3.1 0 Pe rio di c st af f t ra in in g an d sk ill d ev el op m en t. 30 0, 00 0 30 0, 00 0 60 0, 00 0 3.1 1 Se cu re lo ng t er m fu nd in g. 25 0, 00 0 25 0, 00 0 3.1 2 Re gu la r g ro un d tr ut hi ng o f t he re le as ed v ul tu re . 30 0, 00 0 30 0, 00 0 40 0, 00 0 40 0, 00 0 40 0, 00 0 1,8 00 ,0 00 3.1 3 Sa fe ty a nd H yg ie ne e va lu at io n of th e re le as e si te . 20 0, 00 0 20 0, 00 0 40 0, 00 0 Ob je ct iv e 4: P ro m ot e sa fe fo od s up pl y to v ul tu re s 4.1 M ai nt ai n al l V SF S an d ot he r f ee di ng s ite s in th e we st er n lo wl an ds . 50 0, 00 0 50 0, 00 0 50 0, 00 0 50 0, 00 0 50 0, 00 0 2, 50 0, 00 0 4. 2 Ad vo ca te o n ef fi c ie nt re gu la to ry m ec ha ni sm to b an o th er NS AI Ds s ho wn to v ul tu re t ox ic . 20 0, 00 0 10 0, 00 0 10 0, 00 0 10 0, 00 0 10 0, 00 0 60 0, 00 0 4. 3 Ex pa nd V SZ in iti at iv es in to th e ea st er n lo wl an ds . 30 0, 00 0 50 0, 00 0 50 0, 00 0 1,3 00 ,0 00 4. 4 Pr op er m an ag em en t o f c ar ca ss d um ps . 60 0, 00 0 60 0, 00 0 60 0, 00 0 60 0, 00 0 60 0, 00 0 3, 00 0, 00 0 4. 5 Ad vo ca te to p ro vi de d ea d liv es to ck c ar ac as s fo r v ul tu re s. 10 0, 00 0 10 0, 00 0 10 0, 00 0 10 0, 00 0 10 0, 00 0 50 0, 00 0 4. 6 M an ag em en t o f w ild a ni m al c ar ca ss es in p ro te ct ed a nd n on pr ot ec te d ar ea s. 10 0, 00 0 10 0, 00 0 10 0, 00 0 10 0, 00 0 10 0, 00 0 50 0, 00 0 VULTURE CONSERVATION ACTION PLAN (2023-2027) 45 Ob je ct iv e 5: H ab ita t C on se rv at io n an d sa fe gu ar di ng fr om p ow er in fra st ru ct ur e 5.1 Pr ep ar e an d im pl em en t s ite s pe ci fi c m an ag em en t p la n in id en tifi e d pr io rit y ar ea s. 50 0, 00 0 50 0, 00 0 50 0, 00 0 50 0, 00 0 50 0, 00 0 2, 50 0, 00 0 5. 2 Up da te in fo rm at io n on p re vi ou sl y kn ow n, c ur re nt a nd po te nt ia l h ab ita t. 10 0, 00 0 10 0, 00 0 10 0, 00 0 10 0, 00 0 10 0, 00 0 50 0, 00 0 5. 3 Co nt ro l c ut tin g of th e ne st in g tr ee s in th ei r n es tin g ha bi ta t. 50 ,0 00 50 ,0 00 10 0, 00 0 5. 4 En co ur ag e an d su pp or t l oc al c om m un iti es to m an ag e an d pr ot ec t t he h ab ita t. 20 0, 00 0 10 0, 00 0 10 0, 00 0 20 0, 00 0 20 0, 00 0 80 0, 00 0 5. 5 Aw ar en es s ca m pa ig n, S en si tiz e an d aw ar e lo ca l f or es t u se r gr ou ps a nd o th er s ta ke ho ld er s. 20 0, 00 0 30 0, 00 0 20 0, 00 0 30 0, 00 0 20 0, 00 0 1,2 00 ,0 00 5. 6 Pr ot ec t t he n es tin g si te w ith a ll th e po ss ib le d is tu rb an ce s. 20 0, 00 0 20 0, 00 0 10 0, 00 0 50 0, 00 0 5. 7 In fo rm at io n co lle ct io n on th e di st rib ut io n of p ow er li ne s in vu ltu re h ab ita t. 30 0, 00 0 10 0, 00 0 10 0, 00 0 10 0, 00 0 20 0, 00 0 80 0, 00 0 5. 8 Se ns iti vi ty m ap pi ng o f t hr ea te ne d vu ltu re s ag ai ns t h yd ro po we r an d tra ns m is si on li ne s. 30 0, 00 0 30 0, 00 0 30 0, 00 0 3, 00 0, 00 0 30 0, 00 0 4, 20 0, 00 0 5. 9 Em pl oy m iti ga tio n m ea su re s to p re ve nt e le ct ro cu tio n in a re as wh er e it oc cu rs . 30 0, 00 0 10 0, 00 0 30 0, 00 0 70 0, 00 0 Ob je ct iv e 6: S en si tiz e St ak eh ol de rs a nd B ui ld th ei r C ap ac ity 6.1 Co nt in ue to ra is e aw ar en es s of th e di cl of en ac a nd o th er NS AI Ds p ro bl em . 15 0, 00 0 15 0, 00 0 15 0, 00 0 15 0, 00 0 15 0, 00 0 75 0, 00 0 6. 2 Co nt in ue to ra is e aw ar en es s of v ul tu re s an d th e ec os ys te m se rv ic e th ey p ro vi de . 15 0, 00 0 15 0, 00 0 15 0, 00 0 15 0, 00 0 15 0, 00 0 75 0, 00 0 6. 3 Ad vo ca cy to G ov er nm en t O ffi ci al / Or ga ni za tio n (L oc al Go ve rn m en t, DF O, A ni m al a nd L iv es to ck In st itu tio ns , N at io na l Pa rk s ta ff, Tr an s bo un da ry ). 20 0, 00 0 20 0, 00 0 40 0, 00 0 6. 4 Ge ne rin g Ci tiz en S ci en tis t. 20 0, 00 0 20 0, 00 0 20 0, 00 0 20 0, 00 0 20 0, 00 0 1,0 00 ,0 00 VULTURE CONSERVATION ACTION PLAN (2023-2027)46 6. 5 Es ta bl is h Vu ltu re S te wa rd sh ip in iti at iv e at im po rt an t n es tin g si te s in th e we st er n an d ea st er n lo wl an ds . 30 0, 00 0 30 0, 00 0 30 0, 00 0 30 0, 00 0 30 0, 00 0 1,5 00 ,0 00 6. 6 Es ta bl is h in fo rm at io n ce nt er s at a ll VS FS , o th er fe ed in g si te s an d Vu ltu re S te wa rd sh ip S ite s. 30 0, 00 0 30 0, 00 0 20 0, 00 0 30 0, 00 0 30 0, 00 0 1,4 00 ,0 00 6. 7 Ad vo ca te th e in te gr at io n of v ul tu re c on se rv at io n in to co m m un ity fo re st m an ag em en t. 40 0, 00 0 40 0, 00 0 40 0, 00 0 40 0, 00 0 40 0, 00 0 2, 00 0, 00 0 6. 8 Pr ov id e ne ce ss ar y kn ow le dg e, s ki lls a nd m at er ia ls fo r v ul tu re co ns er va tio n to in di vi du al s an d co m m un iti es c on tr ib ut in g to vu ltu re c on se rv at io n. 30 0, 00 0 30 0, 00 0 30 0, 00 0 30 0, 00 0 30 0, 00 0 1,5 00 ,0 00 6. 9 Re co gn ize a nd re wa rd c om m un iti es a nd in di vi du al s fo r t he ir ef fo rt in v ul tu re c on se rv at io n. 20 0, 00 0 20 0, 00 0 20 0, 00 0 20 0, 00 0 20 0, 00 0 1,0 00 ,0 00 6.1 0 Ou tr ea ch M at er ia l p ro du ct io n an d di st rib ut io n. 35 0, 00 0 35 0, 00 0 35 0, 00 0 35 0, 00 0 35 0, 00 0 1,7 50 ,0 00 Ob je ct iv e 7: Bu ild P ar tn er sh ip a t L oc al , N at io na l a nd In te rn at io na l L ev el 7.1 Se cu re 5 % o f t he g ov er nm en t b ud ge t f or v ul tu re c on se rv at io n. 25 0, 00 0 25 0, 00 0 7.2 M ai nt ai n go od re la tio ns hi ps w ith IN GO s th at p ro vi de fu nd s an d/ or e xp er tis e th ro ug h m ee tin g ob je ct iv es a nd ti m el y re po rt in g. 10 0, 00 0 10 0, 00 0 10 0, 00 0 10 0, 00 0 10 0, 00 0 50 0, 00 0 7.3 Pa rt ne r w ith n at io na l, re gi on al a nd /o r i nt er na tio na l or ga ni sa tio ns to s ec ur e bi g fu nd s. 10 0, 00 0 10 0, 00 0 10 0, 00 0 10 0, 00 0 10 0, 00 0 50 0, 00 0 7.4 Tr an sb ou nd ar y co lla bo ra tio n es pe ci al ly w ith In di an p ar tn er s wo rk in g wi th in 10 0k m fr om p ot en tia l r el ea se s ite s in N ep al . 50 0, 00 0 50 0, 00 0 50 0, 00 0 1,5 00 ,0 00 7.5 Pa rt ic ip at e in n at io na l, re gi on al a nd in te rn at io na l m ee tin gs an d wo rk sh op s to b ui ld n et wo rk s an d ex pe rt is e. 50 0, 00 0 50 0, 00 0 50 0, 00 0 50 0, 00 0 50 0, 00 0 2, 50 0, 00 0 VULTURE CONSERVATION ACTION PLAN (2023-2027) 47 Ob je ct iv e 8: S tr en gt he n th e Vu ltu re S af e Zo ne (V SZ ) N et wo rk 8.1 De ve lo p tra ns b ou nd ar y co op er at iv e wi th o rg an is at io n in In di a to e xt en d VS Z co ns er va tio n ac tio ns . 20 0, 00 0 20 0, 00 0 20 0, 00 0 20 0, 00 0 20 0, 00 0 1,0 00 ,0 00 8. 2 Pa rt ne rin g wi th c om m un iti es , v et p ro fe ss io na ls , G ov er nm en t ag en ci es a nd o th er c on se rv at io n or ga ni sa tio ns . 10 0, 00 0 10 0, 00 0 10 0, 00 0 10 0, 00 0 10 0, 00 0 50 0, 00 0 8. 3 M on ito rin g NS AI Ds u se a nd e ffe ct iv en es s of b an o f h ar m fu l NS AI Ds a ro un d th e pr op os ed V SZ . 20 0, 00 0 20 0, 00 0 20 0, 00 0 20 0, 00 0 20 0, 00 0 1,0 00 ,0 00 8. 4 Co m m un ity m an ag ed V ul tu re s af e fe ed in g si te s an d sa fe ca rc as s di sp os al s ite s. 30 0, 00 0 30 0, 00 0 30 0, 00 0 30 0, 00 0 30 0, 00 0 1,5 00 ,0 00 8. 5 Aw ar en es s, se ns iti za tio n an d ad vo ca cy . 20 0, 00 0 10 0, 00 0 10 0, 00 0 20 0, 00 0 10 0, 00 0 70 0, 00 0 8. 6 St re ng th en c om m un iti es fo r v ul tu re s af e zo ne m an ag em en t. 20 0, 00 0 20 0, 00 0 20 0, 00 0 20 0, 00 0 20 0, 00 0 1,0 00 ,0 00 8. 7 Ta gg ed v ul tu re m ov em en t m on ito rin g an d its a ss es sm en t f or fo ra gi ng a nd b re ed in g si te . 20 0, 00 0 20 0, 00 0 20 0, 00 0 20 0, 00 0 20 0, 00 0 1,0 00 ,0 00 8. 8 M on ito rin g th e su rv iv al o f a ll ta gg ed b ird s an d fi n d th e ca us es fo r a ny m or ta lit ie s. 20 0, 00 0 20 0, 00 0 20 0, 00 0 20 0, 00 0 20 0, 00 0 1,0 00 ,0 00 8. 9 VS Z in iti at iv e ex pa nd ed in to th e pV SZ a nd to e as te rn lo wl an ds . 50 ,0 00 50 0, 00 0 55 0, 00 0 VULTURE CONSERVATION ACTION PLAN (2023-2027)48 VULTURE CONSERVATION ACTION PLAN (2023-2027) 49 The Vulture Conservation Action Plan (2023-2027) has been prepared in collaboration with:

Vulture Conservation Action Plan (2023-2027) · Nelum