Arctic Council Working Group Recommendations
| Project | Type | # | Outcome | Report | Year | FEC |
|---|---|---|---|---|---|---|
| CBMP Terrestrial Biodiversity Monitoring | Key finding | The range and complexity of drivers affecting Arctic terrestrial biodiversity signals the need for comprehensive, integrated, ecosystem-based monitoring programs, coupled with targeted research projects to help decipher causal patterns of change. | State of the Arctic Terrestrial Biodiversity: Key Findings and Advice for Monitoring | 2021 | ||
| Arctic Biodiversity Assessment (ABA) | Key finding | 2 | Although the majority of Arctic species examined in this report are currently stable or increasing, some species of importance to Arctic people or species of global significance are declining. | Arctic Biodiversity Trends 2010 – Selected indicators of change | 2010 | |
| Arctic Biodiversity Assessment (ABA) | Key finding | 1 | Increase opportunities for cross-cultural learning, understanding and trust building. | Arctic Traditional Knowledge and Wisdom: Changes in the North American Arctic | 2017 | |
| Resilience and Management of Arctic Wetlands (RAW) | Key finding | Comprehensive information on Arctic wetlands ecosystems is currently lacking but needed to adequately identify the location and type of wetlands with high levels of accuracy. Recent developments in the use of geospatial data and artificial intelligence provide the basis for substantial improvements in mapping of the extent and condition of Arctic wetlands, opening up valuable opportunities for pan-Arctic collaboration to improve wetlands inventories and keep them up-to-date. | Resilience and Management of Arctic Wetlands Phase 2 Report | 2021 | ||
| Resilience and Management of Arctic Wetlands (RAW) | Key finding | 10 | Substantial and rapid benefits for ecosystem services such as climate stability, biodiversity conservation and hydrological systems could be gained through restoration of drained or degraded Arctic peatlands. Degraded wetlands exist in all Arctic states and are particularly common in Boreal regions where extensive drainage for forestry, mining or peat extraction has occurred, or in Tundra where vulnerable permafrost wetlands have been degraded by unsustainable human land-use. Re-wetting of artificially drained or restoration of damaged wetlands could lead to substantial increases in natural carbon sink capacities. To achieve long-term success, restoration efforts should be planned together with conservation of undamaged systems as part of a landscape scale approach to sustainable management. | Resilience and Management of Arctic Wetlands: Key Findings and Recommendations | 2021 | |
| Arctic TEEB | Key finding | 3.4 | Governance: Key Finding 3.4. Recognizing, demonstrating and capturing the diverse values of ecosystem services in policy instruments for strategic planning and integrated management of natural resources and space can help reconcile biodiversity conservation with development. | The Economics of Ecosystems and Biodiversity (TEEB) for the Arctic: A Scoping Study Executive Summary | 2015 | |
| CBMP Terrestrial Biodiversity Monitoring | Key finding | “White” geese (Chen) are most numerous (17.2 million individuals of 3 species) and all 6 populations have increased in the last 10 years. | A Global Audit of the Status and Trends of Arctic And Northern Hemisphere Goose Populations | 2018 | ||
| Key finding | 4 | Different environmental changes are occurring within different cultural contexts creating diverse impacts; as such adaptive actions need to be based on local realities and priorities | Project Summary: Bering Sea Sub-Network II | 2015 | ||
| CBMP Marine Biodiversity Monitoring | Key finding | Food resources are being lost for many Arctic species in Arctic marine environments. Many species have to travel further and expend more energy to feed, leading to concerns about individual health and potential effects at the population level | State of the Arctic Marine Biodiversity: Key Findings and Advice for Monitoring | 2017 | ||
| Arctic Biodiversity Assessment (ABA) | Key finding | 5 | Pollution from both long-range transport and local sources threatens the health of Arctic species and ecosystems. | Arctic Biodiversity Assessment: Report for Policy Makers | 2013 | |
| Key finding | Conservation of biodiversity and of the ecosystem services it provides requires a long-term perspective and sustained actions at many different temporal and spatial scales. | Arctic Biodiversity Congress 2014, Co-Chairs Report | 2014 | |||
| Arctic Species Trend Index (ASTI) | Key finding | 4 | Shorebirds are in decline overall (-10%), with negative trends in the Americas and East Asia (-10% and -70%). Populations of this group are faring better in Africa-Eurasia, where abundance is 40% higher compared to 1970. | Arctic Species Trend Index: Migratory Birds Index | 2015 | |
| Resilience and Management of Arctic Wetlands (RAW) | Key finding | 3 | Anthropogenic climate change is a serious threat to Arctic wetland ecosystems and exacerbates many other threats. Widespread climate change impacts in Arctic wetlands are ongoing and projected to increase in this century and reducing greenhouse gas emissions is necessary to limit these impacts. Climate-driven permafrost thaw and increased drought conditions impacting wetland ecosystems will cause greater fire occurrences and shifts in hydrological flows, affecting wetland ecosystem services and biodiversity. Sea level change and declines in sea ice are driving increases in coastal erosion that threatens many coastal wetlands. Thawing permafrost is projected to transform peatlands from a net sink of greenhouse gases to a net source lasting for several centuries. | Resilience and Management of Arctic Wetlands: Key Findings and Recommendations | 2021 | |
| Resilience and Management of Arctic Wetlands (RAW) | Key finding | 1.2.2 | Arctic Indigenous Wetlands Use: Indigenous Peoples have significant ties to wetland protected areas in the Arctic and acknowledging and fostering these relationships in partnership with management authorities can strengthen outcomes. | Arctic Wetlands and Indigenous Peoples Study: An assessment of Indigenous engagement in wetland protected areas | 2021 | |
| Arctic TEEB | Key finding | 2.3 | Arctic ecosystem services: Although syntheses, guidelines and analyses of policy options at the pan-Arctic scale can raise the profile of ecosystem services and provide direction, work on ecosystem services is most effective when it builds on analysis at smaller scales. | The Economics of Ecosystems and Biodiversity (TEEB) for the Arctic: A Scoping Study Executive Summary | 2015 | |
| Arctic TEEB | Key finding | 5.1 | Policy focus: Key Finding 5.1. Policy related to increasing and changing development patterns in the Arctic wouldbenefit from incorporation of consideration of ecosystem services. Participants in this scoping projectidentified a list of policy areas for further consideration, and two of these were assessed as ‘policyexamples’ through a TEEB approach, at a broad scoping level: expanding shipping and oil and gasdevelopment in the marine environment, and industrial development in the North American Arctic.) | The Economics of Ecosystems and Biodiversity (TEEB) for the Arctic: A Scoping Study Executive Summary | 2015 | |
| CBMP Terrestrial Biodiversity Monitoring | Key finding | The most urgent priorities for the future are to (i) improve our knowledge of population distributions to better inform our definitions of discrete flyway populations; (ii) implement effective mechanisms to at least periodically measure abundance for all northern hemisphere goose populations to assess trends over time; (iii) initiate research to identify factors responsible for declining trends in populations of concern, and (iv) evaluate potential negative effects of overabundant goose populations on habitat and sympatric species. | A Global Audit of the Status and Trends of Arctic And Northern Hemisphere Goose Populations | 2018 | ||
| CBMP Freshwater Biodiversity Monitoring | Key finding | In countries where routine government monitoring is limited or does not occur, data must come from other sources (e.g., academic research), where unsecure funding often leads to single-event sampling, meaning that change over time cannot be examined. | State of the Arctic Freshwater Biodiversity: Key Findings and Advice for Monitoring | 2016 | ||
| Arctic Biodiversity Assessment (ABA) | Key finding | 4 | Since 1991, the extent of protected areas in the Arctic has increased, although marine areas remain poorly represented. | Arctic Biodiversity Trends 2010 – Selected indicators of change | 2010 | |
| Arctic Biodiversity Assessment (ABA) | Key finding | 3 | Develop effective partnerships and/or formalized systems of sharing among indigenous peoples and scientists to more fully engage this wide range of human intelligence to understand the complexities of managing biodiversity in the Arctic; for example, TK&W can provide early warnings of environmentalchange, indicate connections between phenomena, and fill data gaps. | Arctic Traditional Knowledge and Wisdom: Changes in the North American Arctic | 2017 |