Arctic Council Working Group Recommendations
| Project | Type | # | Outcome | Report | Year | FEC |
|---|---|---|---|---|---|---|
| Arctic Biodiversity Assessment (ABA) | Recommendation | 2 | Identify measures for detecting early warnings of biodiversity change and triggering conservation actions.Move towards a stronger reliance on early warnings of ecosystem change, rather than on population trends as triggers for making decisions. Aside from catastrophic die-offs and breeding failure, impacts from changes in sea ice are often incremental, such as a reduced rate of reproduction or survival, or less energy intake from prey. Impacts may take years to be detected in population trends, especially for long-lived animals. Measures such as reduced body condition or changes in ice-dependent prey species are evidence of impacts that can be acted on before declines are detected in abundance or distribution. In some cases these earlier actions will prevent or lessen population declines. Factors to consider in selecting such measures of change include long-term costs and benefits, support by research, ability to be updated, and suitability for determining thresholds for action. | Life Linked to Ice: A guide to sea-ice-associated biodiversity in this time of rapid change | 2013 | |
| Arctic Biodiversity Assessment (ABA) | Recommendation | 3 | Make more effective use of local and traditional knowledge in Arctic Council assessments and, more broadly, in ecological management. We need the best available knowledge to detect and respond to rapid Arctic ecosystem change. Local and traditional knowledge sources, by their nature, bring a depth of knowledge and understanding of ecosystems, as well as early warnings of change, that complement science-based studies. However, these knowledge sources are generally underutilized in assessment and management except at the scale of the knowledge holders | Life Linked to Ice: A guide to sea-ice-associated biodiversity in this time of rapid change | 2013 | |
| Arctic Biodiversity Assessment (ABA) | Recommendation | 4 | Target resource managers when communicating research, monitoring and assessment findings. Increase efforts to communicate results of research and monitoring relevant to conservation of sea-ice associated biodiversity. Focus particularly on meeting the information needs of those making on-the-ground wildlife conservation decisions on, for example, conditions of development permits or fish and wildlife harvest regulations. Available information, including from recent Arctic Council assessments, may be hard for managers to sift through or to know what is most relevant to them. Work in this area should engage users of the information in designing content and delivery and should consider methods beyond print media. It should take into account time and resource constraints of the users and considerations such as keeping information up to date. Communication may best be delivered at a national or regional level, but benefits and efficiencies of collaboration through Arctic Council could be explored. | Life Linked to Ice: A guide to sea-ice-associated biodiversity in this time of rapid change | 2013 | |
| Arctic Biodiversity Assessment (ABA) | Key finding | 1 | Unique Arctic habitats for flora and fauna, including sea ice, tundra, thermokarst ponds and lakes, and permafrost peatlands have been disappearing over recent decades. | Arctic Biodiversity Trends 2010 – Selected indicators of change | 2010 | |
| 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 | 3 | Climate change is emerging as the most far reaching and significant stressor on Arctic biodiversity. However, contaminants, habitat fragmentation, industrial development, and unsustainable harvest levels continue to have impacts. Complex interactions between climate change and other factors have the potential to magnify impacts on biodiversity. | Arctic Biodiversity Trends 2010 – Selected indicators of change | 2010 | |
| 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 | 5 | Changes in Arctic biodiversity are creating both challenges and opportunities for Arctic peoples. | Arctic Biodiversity Trends 2010 – Selected indicators of change | 2010 | |
| Arctic Biodiversity Assessment (ABA) | Key finding | 6 | Long-term observations based on the best available traditional and scientific knowledge are required to identify changes in biodiversity, assess the implications of observed changes, and develop adaptation strategies. | Arctic Biodiversity Trends 2010 – Selected indicators of change | 2010 | |
| Arctic Biodiversity Assessment (ABA) | Key finding | 7 | Changes in Arctic biodiversity have global repercussions. | Arctic Biodiversity Trends 2010 – Selected indicators of change | 2010 | |
| Arctic Species Trend Index (ASTI) | Key finding | 1 | The Arctic Species Trend Index (ASTI): 2011 update. 1.1 Average abundance of Arctic vertebrates increased from 1970 until 1990 then remained fairly stable through 2007, as measured by the ASTI 2011. 1.2 When species abundance is grouped by broad ecozones, a different picture emerges, with low Arctic species abundance increasing in the first two decades much more than high Arctic and sub Arctic species abundance. The low Arctic index has stabilized since the mid-1990s while the high Arctic index appears to be recovering in recent years and the sub Arctic index has been declining since a peak in the mid-1980s. 1.3 The trend for Arctic marine species is similar to that of the overall ASTI, while the trend for terrestrial species shows a quite different pattern: a steady decline after the early 1990s to a level below the 1970 baseline by 2005. | The Arctic Species Trend Index 2011: Key findings from an in-depth look at marine species and development of spatial analysis techniques | 2012 | |
| Arctic Species Trend Index (ASTI) | Key finding | 2 | Tracking trends in Arctic marine vertebrates. 2.1 The trend for marine fish is very similar to the trend for all marine species, increasing from 1970 to about 1990 and then levelling off. This indicates that the ASTI is strongly influenced by fish trends. Overall, marine mammals also increased, while marine birds showed less change. 2.2 The three ocean regions, Pacific, Atlantic, and Arctic, differed significantly in average population trends with an overall decline in abundance in the Atlantic, a small average increase in the Arctic and a dramatic increase in the Pacific. These differences seem to be largely driven by variation in fish population abundance—there were no significant regional differences for birds or mammals. 2.3 Pelagic fish abundance appears to cycle on a time frame of about 10 years. These cycles showeda strong association with a large-scale climate oscillation. 2.4 The ASTI data set contains population trends for nine sea ice associated species. There were mixed trends among the 36 populations with just over half showing an overall decline. 2.5 The Bering Sea and Aleutian Island (BSAI) region of the Pacific Ocean is well studied, providing an opportunity to examine trends in more detail. Since 1970, BSAI marine fish and mammals showed overall increases, while marine birds declined. However, since the late 1980s, marine mammal abundance has declined while marine fish abundance has largely stabilized. | The Arctic Species Trend Index 2011: Key findings from an in-depth look at marine species and development of spatial analysis techniques | 2012 | |
| Arctic Species Trend Index (ASTI) | Key finding | 3 | Tracking trends through space and time. 3.1 Spatial analysis of the full ASTI data set (1951 to 2010) started with an evaluation of vertebrate population trend data from around the Arctic. The maps produced from this analysis provide information useful for identifying gaps and setting priorities for biodiversity monitoring programs. 3.2 Mapping trends in vertebrate populations provides information on patterns of biodiversity change over space and time, especially when examined at regional scales. 3.3 Understanding of the causes of Arctic vertebrate population change can be improved by expanding the spatial analysis of ASTI data to include spatial data on variables that represent driversof biodiversity change. | The Arctic Species Trend Index 2011: Key findings from an in-depth look at marine species and development of spatial analysis techniques | 2012 | |
| Arctic Migratory Birds Initiative (AMBI) | Advice | 1 | Methods to monitor plastic pollution in seabirds – Standardized methods (OSPAR 2015; Provencher et al. 2017, 2019) should be used where possible to make data comparable across spatially and temporally. | Plastic Pollution in Seabirds: Developing a program to monitor plastic pollution in seabirds in the pan-Arctic region | 2021 | |
| Arctic Migratory Birds Initiative (AMBI) | Advice | 2 | Monitoring temporal trends in plastic ingestion: The northern fulmar, thick-billed murre and black-legged kittiwake should be monitored for temporal trends in plastic pollution ingestion. | Plastic Pollution in Seabirds: Developing a program to monitor plastic pollution in seabirds in the pan-Arctic region | 2021 | |
| Arctic Migratory Birds Initiative (AMBI) | Advice | 3 | Monitoring temporal trends in plastic ingestion: The northern fulmar, thick-billed murre and black-legged kittiwake should be monitored for temporal trends in plastic pollution ingestion. | Plastic Pollution in Seabirds: Developing a program to monitor plastic pollution in seabirds in the pan-Arctic region | 2021 | |
| Arctic Migratory Birds Initiative (AMBI) | Advice | 4 | Monitoring nest incorporation and entanglement: Black-legged kittiwake and northern gannet (Morus bassanus) nests should be monitored for nest incorporation of and entanglement in plastic pollution. | Plastic Pollution in Seabirds: Developing a program to monitor plastic pollution in seabirds in the pan-Arctic region | 2021 | |
| Arctic Migratory Birds Initiative (AMBI) | Advice | 5 | Monitoring microplastics and plastic-associated contaminants: Northern fulmars, thick-billed murres, black-legged kittiwakes and common eiders should be monitored for microplastics and plastic-associated contaminants. | Plastic Pollution in Seabirds: Developing a program to monitor plastic pollution in seabirds in the pan-Arctic region | 2021 | |
| Arctic Migratory Birds Initiative (AMBI) | Advice | 6 | Monitoring point sources of plastic pollution: Glaucous gull (Larus hyperboreus), great skua (Stercorarius skua) and other gull species that feed at landfills and other urban or rural sites, pellets/regurgitations should be monitored for plastic pollution near point sources to track local trends in plastic pollution. | Plastic Pollution in Seabirds: Developing a program to monitor plastic pollution in seabirds in the pan-Arctic region | 2021 | |
| Arctic Migratory Birds Initiative (AMBI) | Advice | 7 | Monitoring species of high conservation concern – Leach’s storm-petrels should be monitored where possible for potential effects of plastic pollution. | Plastic Pollution in Seabirds: Developing a program to monitor plastic pollution in seabirds in the pan-Arctic region | 2021 |