Recommendations
| Project | Type | # | Outcome | Report | Year | FEC |
|---|---|---|---|---|---|---|
| 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 | |
| Resilience and Management of Arctic Wetlands (RAW) | Key finding | The key obstacles to scaling up and expanding wetlands restoration and management efforts in the Arctic are not due to a lack of knowledge about wetlands ecosystems processes and functions, or steps that can be taken to improve their status. Policy design and difficulties with implementation appear often to be obstacles, however, and accurate, up-to-date mapping is needed to target policy initiatives. | Resilience and Management of Arctic Wetlands Phase 2 Report | 2021 | ||
| Resilience and Management of Arctic Wetlands (RAW) | Key finding | 12 | There is a need for new pan-Arctic wetland maps based on a uniform approach, thus ensuring comparable accuracy and data quality across the full Arctic domain. Such mapping efforts should ideally train and validate algorithms using existing national wetland inventories, relevant institutional data, inclusive of Indigenous Knowledge and/or input from Arctic communities. Maps are needed that show the spatial extent of discrete wetland complexes at high resolution and should separate mineral wetlands from organic wetlands (peatlands). On the shorter term, new maps of wetland extent will be bound to one specific classification system; it is not possible to address the diversity of existing systems. Over the longer term, boundaries between maps and monitoring dissolve. Spatial wetland data can be stored in spatial databases that allow flexible adaptation to different classification systems. | Resilience and Management of Arctic Wetlands: Key Findings and Recommendations | 2021 | |
| Arctic TEEB | Key finding | 3.6 | Governance: Key Finding 3.6. Mainstreaming of nature’s values by means of ecosystem services requires adjustments to existing policies and instruments as well as the development of new ones. | The Economics of Ecosystems and Biodiversity (TEEB) for the Arctic: A Scoping Study Executive Summary | 2015 | |
| CBMP Terrestrial Biodiversity Monitoring | Key finding | “Grey” geese (Anser) comprise 35 populations of 8.1-8.4 million individuals, of which 15 have declined in the last 10 years, especially in East Asia. | A Global Audit of the Status and Trends of Arctic And Northern Hemisphere Goose Populations | 2018 | ||
| Key finding | 6 | Regulations that impact communities ought to be flexible to allow for adaptation to change and ought to include meaningful local voice through instruments such as co-management to support the food security and sovereignty of indigenous communities | Project Summary: Bering Sea Sub-Network II | 2015 | ||
| CBMP Marine Biodiversity Monitoring | Key finding | Northward movement is easier for more mobile openwater species. Open water species such as polar cod, are more mobile compared to those linked to shelf regions, such as benthic species including some fishes for which suitable habitat may be unavailable if they move northward. | State of the Arctic Marine Biodiversity: Key Findings and Advice for Monitoring | 2017 | ||
| CBMP Terrestrial Biodiversity Monitoring | Key finding | Climate change is the overwhelming driver of change in terrestrial Arctic ecosystems, causing diverse, unpredictable, and significant impacts that are expected to intensify. | State of the Arctic Terrestrial Biodiversity: Key Findings and Advice for Monitoring | 2021 | ||
| Arctic Biodiversity Assessment (ABA) | Key finding | 7 | Overharvest was historically the primary human impact on many Arctic species, but sound management has successfully addressed this problem in most, but not all, cases. | Arctic Biodiversity Assessment: Report for Policy Makers | 2013 | |
| Arctic Species Trend Index (ASTI) | Key finding | 6 | In the Wadden Sea, Arctic bird abundance is 75% higher in 2010 than in 1980, but the trend has been following a negative trajectory since 2002. | Arctic Species Trend Index: Migratory Birds Index | 2015 | |
| Resilience and Management of Arctic Wetlands (RAW) | Key finding | 5 | In some regions, Arctic wetlands are already degraded by human land use and an ever growing human footprint poses threats to wetland functioning. This damage occurs in both Arctic and Boreal zones and arises from a number of threats such as expansion of forestry, agriculture, hydropower, extraction of peat, fossil fuels or minerals, threats to coastal wetlands from increased Arctic shipping and construction of new infrastructure. Wetlands are also vulnerable to human disturbances to permafrost or adjacent upland habitats and changes to the water balance or hydrological connectivity that can transform wetland function. Drained wetlands release carbon to the atmosphere instead of storing it, and the negative effect lasts for decades to centuries. Other losses of function include loss of biodiversity, changes to habitats and reduced capacity to buffer floods or droughts. | Resilience and Management of Arctic Wetlands: Key Findings and Recommendations | 2021 | |
| Resilience and Management of Arctic Wetlands (RAW) | Key finding | 1.2.4 | Arctic Indigenous Participation in Wetlands Conservation: Engaging Indigenous leadership and communities in participatory processes can strengthen conservation strategies and contribute to forwarding conservation objectives and goals. | Arctic Wetlands and Indigenous Peoples Study: An assessment of Indigenous engagement in wetland protected areas | 2021 | |
| Arctic TEEB | Key finding | 2.5 | Arctic ecosystem services: Reduction of greenhouse gases remains a top priority for conserving ecosystem services. | The Economics of Ecosystems and Biodiversity (TEEB) for the Arctic: A Scoping Study Executive Summary | 2015 | |
| Arctic TEEB | Key finding | 6.2 | Way forward: Early policy-maker involvement is crucial for designing effective approaches to policy change. This includes policy-makers at international and national levels, and includes people working on policy not directly related to environmental management, such as trade, business and fiscal policy. | The Economics of Ecosystems and Biodiversity (TEEB) for the Arctic: A Scoping Study Executive Summary | 2015 | |
| CBMP Terrestrial Biodiversity Monitoring | Key finding | For this reason we urge wider gathering of age ratio data, and marking programmes to provide annual assessments of reproductive success and survival, particularly amongst populations showing declines. | A Global Audit of the Status and Trends of Arctic And Northern Hemisphere Goose Populations | 2018 |
Arctic Council Working Group