Displaced organisms are individuals and groups of animals, plants, or fungi that have been recovered from legal or illegal trade, driven from their habitats through habitat destruction or human-wildlife conflicts, displaced or incapacitated by catastrophic events (fires, floods, and extreme weather events) or climate change, or captured or collected by humans. The full scale of irresponsibly translocated organisms is difficult to measure as most are unrecorded. Following the steps in this guidance, attempts can be made to maximise the conservation benefit of translocations of displaced organisms.
Societies around the globe harvest wild species, to a greater or lesser extent, for food, building materials, healthcare, medicines, pest control, ornamentation, income, recreation, and cultural and spiritual purposes. While this use of wild species directly contributes to the well-being of billions of people globally, over-exploitation of wild species is one of the key drivers of biodiversity loss. The IUCN Guidelines on harvesting threatened species advise decision-makers on whether, how and what to harvest to ensure the sustainable use of threatened animal, plant and fungal species. Drawing on insights from the IPBES Sustainable Use Assessment, they complement and expand on existing guidance and tools, such as the Guidelines for the Appropriate Use of IUCN Red List Data in Harvesting of Threatened Species and recent CITES guidance on the conduct of Non-Detriment Findings.
Protected and conserved areas (PCAs) have been proven to provide enormous value to nature, people and the economy. They are an effective means by which species, habitats and ecosystems can be conserved, restored and sustainably utilised. This Guide provides detailed frameworks, descriptions and insights into the use of conservation finance solutions to achieve PCA outcomes. The guidance presents the case for PCA investment and sustainable finance, describes the role and use of finance and economics to achieve PCA outcomes, and presents guidance on how to conduct strategic and practical financial planning in support of these outcomes.
This document provides broad guidance on surveillance of infectious and non-infectious wildlife diseases, pathogens and toxic agents to assist in the implementation of a national surveillance programme for free-ranging wildlife. It is intended to promote a common understanding, which can serve as a foundation for training and operational procedures. While this guidance is geared to surveillance of free-ranging wildlife (whether in spaces managed by the public or private sector), much of the information is also generally applicable to (though not comprehensive for) wild animals in captive settings.
This report presents findings from an assessment of the biodiversity conservation potential of four project sites: Lobaye, Mambéré-Kadéï, Ombella-Mpoko, and Sangha-Mbaéré located in the Bangui region of the Central African Republic (CAR). This assessment was done using the Species Threat Abatement and Recovery (STAR) metric, which employs high-resolution imagery and an approach to modelling species’ Area of Habitat (AOH) that was revised after June 2020 among other enhancements. This work was undertaken to better inform threat abatement and restoration planning and implementation at the partner project sites, and as part of a wider effort to pilot and strengthen the use of STAR as a tool for restoration and conservation practitioners, communities, investors, and policymakers.
Key Biodiversity Areas (KBAs) are sites that contribute significantly to the global persistence of biodiversity. The purpose of the Guidelines for using A Global Standard for the Identification of Key Biodiversity Areas is to ensure that KBA identification is based on consistent, scientifically rigorous yet practical methods. The KBA Guidelines provide an overview of the steps for identifying and delineating KBAs, together with explanation of how the KBA criteria, thresholds and delineation procedures should be applied in practice. The KBA Guidelines should be used hand-in-hand with the KBA Standard (IUCN, 2016).
The Kunming-Montreal Global Biodiversity Framework, adopted in 2022, provides a framework for the effective implementation of the Convention on Biological Diversity (CBD) through four goals and 23 targets. Target 3 (known as the ‘30×30 target’) calls on Parties to conserve at least 30% of terrestrial, inland waters, and coastal and marine areas by 2030. These guidelines are designed to promote good practices relating to identifying, reporting, monitoring and strengthening OECMs. They are intended for use by a wide range of rightsholders and stakeholders to promote understanding of whether a site meets the CBD criteria for identifying an OECM, how to report OECM data at the national and global levels, and how to monitor and strengthen OECMs.
This is the first volume in the WCPA Good Practice Guidelines that is predominantly by rangers, for rangers. The editors worked with partners to collect good practices and stories from rangers worldwide, reflecting global experience and lessons learned. The text focuses on actions that rangers, and to a lesser extent managers, can do themselves. It does not address institutional changes that would need intervention at government level. Whilst the latter are often necessary, decisions are out of the hands of individual rangers. Nor is the guide the last word on the state of play, another global ranger survey is being carried out simultaneously with the production of these guidelines and we will continue to learn about ranger needs, strengths and challenges in the future.
Ce présent ouvrage vise à déterminer la contribution économique des aires protégées et de la biodiversité dans les politiques et stratégies environnementales régionales de l’espace UEMOA-CEDEAO (Union Economique et monétaire Ouest Africaine et de la Mauritanie – Communauté économique des états de l’Afrique de l’Ouest). Pour atteindre les objectifs visés par ce travail, cet ouvrage aborde successivement le rôle de la biodiversité et des aires protégées dans l’amélioration du bien-être des communautés, l’importance de l’évaluation économique du capital naturel et des services écosystémiques et enfin les instruments d’intégration du capital naturel dans la planification et la prise de décision.
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