Recommendations
| Project | Type | # | Outcome | Report | Year | FEC |
|---|---|---|---|---|---|---|
| CBMP Terrestrial Biodiversity Monitoring | Key finding | Most populations showed increasing or stable trends over the last 10 years, but our ability to truly judge these trends is highly variable among populations. | A Global Audit of the Status and Trends of Arctic And Northern Hemisphere Goose Populations | 2018 | ||
| CBMP Terrestrial Biodiversity Monitoring | Key finding | In North America, population estimates are good; trends are generally of the best quality and most populations are increasing or stable. | A Global Audit of the Status and Trends of Arctic And Northern Hemisphere Goose Populations | 2018 | ||
| CBMP Terrestrial Biodiversity Monitoring | Key finding | Most European populations are increasing or stable, yet several populations lack effective count coordination networks to generate annual assessments of total population size and trends. | A Global Audit of the Status and Trends of Arctic And Northern Hemisphere Goose Populations | 2018 | ||
| CBMP Terrestrial Biodiversity Monitoring | Key finding | In Central and Eastern Asia, where the greatest declines are suspected, good population estimates and count data series over sufficient long time horizons to offer a robust basis for generating trends are generally lacking, with the notable exception of excellent count data from Korea and Japan. However, the situation is rapidly improving in China, where count networks and coordination with flyway partners are being established. | A Global Audit of the Status and Trends of Arctic And Northern Hemisphere Goose Populations | 2018 | ||
| CBMP Terrestrial Biodiversity Monitoring | Key finding | Many populations with the poorest population information are those which we suspect are showing the greatest declines. | A Global Audit of the Status and Trends of Arctic And Northern Hemisphere Goose Populations | 2018 | ||
| 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 Terrestrial Biodiversity Monitoring | Key finding | To interpret changes in population size, there is an increasing need to understand whether these are due to shifts in range, changes in reproductive success or changes in annual survival. | A Global Audit of the Status and Trends of Arctic And Northern Hemisphere Goose Populations | 2018 | ||
| 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 | ||
| CBMP Terrestrial Biodiversity Monitoring | Key finding | There is a very clear need to establish or expand annual reporting on population size and demographic trends to make such information accessible to decision makers and stakeholders in a timely fashion. | A Global Audit of the Status and Trends of Arctic And Northern Hemisphere Goose Populations | 2018 | ||
| CBMP Freshwater Biodiversity Monitoring | Key finding | Temperature is the overriding and predominant driver for most FECs, but climate, geographical connectivity, geology, and smaller-scale environmental parameters such as water chemistry are all key drivers of Arctic freshwater biodiversity. | State of the Arctic Freshwater Biodiversity: Key Findings and Advice for Monitoring | 2016 | ||
| CBMP Freshwater Biodiversity Monitoring | Key finding | The vast expanse of the Arctic region in some countries (e.g., Canada, Russia) and the high monetary cost and logistical constraints associated with sampling in some regions (e.g., northern Canada and Russia, Greenland, Svalbard, Faroe Islands) limits the possibility of routine monitoring. This leads to sparse sample coverage in space and time, particularly where funds are not secure. | State of the Arctic Freshwater Biodiversity: Key Findings and Advice for Monitoring | 2016 | ||
| CBMP Freshwater Biodiversity Monitoring | Key finding | All countries have data sets that allow for identification of baseline levels for most FECs, but only a few countries (such as Finland and Sweden) have an extensive spatial coverage and very few countries have long time series. Data collection was not exhaustive, and there are likely additional data that exist for each country that may contribute to the assessment of freshwater biodiversity; however, significant gaps will remain even with a more extensive search of existing data sources. | State of the Arctic Freshwater Biodiversity: Key Findings and Advice for Monitoring | 2016 | ||
| CBMP Freshwater Biodiversity Monitoring | Key finding | Arctic freshwater ecosystems are highly threatened by climate change and human development which can alter the distribution and abundance of species and affect biodiversity and the ecosystem services on which many Arctic peoples depend. | State of the Arctic Freshwater Biodiversity: Key Findings and Advice for Monitoring | 2016 | ||
| CBMP Freshwater Biodiversity Monitoring | Key finding | Available long-term monitoring records and research data indicate that freshwater biodiversity has changed over the last 200 years, with shifts in species composition being less dramatic in areas where temperatures have been more stable. | State of the Arctic Freshwater Biodiversity: Key Findings and Advice for Monitoring | 2016 | ||
| 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 | ||
| CBMP Freshwater Biodiversity Monitoring | Key finding | Instruments such as the European Water Framework Directive promote routine monitoring of lake and river FECs. But where a country, ecoregion, or FEC is not covered by such instruments, monitoring is irregular, has poor spatial coverage, or is absent. | State of the Arctic Freshwater Biodiversity: Key Findings and Advice for Monitoring | 2016 | ||
| CBMP Freshwater Biodiversity Monitoring | Key finding | Patterns of biodiversity vary across the Arctic, but ecoregions that have historically warmer temperatures and connections to the mainland generally have higher biodiversity than those with cold temperatures (high latitude or altitude) or on remote islands. | State of the Arctic Freshwater Biodiversity: Key Findings and Advice for Monitoring | 2016 | ||
| CBMP Freshwater Biodiversity Monitoring | Advice | Monitoring Methods
| State of the Arctic Freshwater Biodiversity: Key Findings and Advice for Monitoring | 2016 | ||
| CBMP Freshwater Biodiversity Monitoring | Advice | Traditional Knowledge (TK)
| State of the Arctic Freshwater Biodiversity: Key Findings and Advice for Monitoring | 2016 | ||
| CBMP Freshwater Biodiversity Monitoring | Advice | Citizen Science
| State of the Arctic Freshwater Biodiversity: Key Findings and Advice for Monitoring | 2016 |
Arctic Council Working Group