Recommendations

Secure intertidal and associated habitat for AMBI priority species at key staging and wintering sites in the Central and East Asian Flyways.

2.1 (Russia): Ensure improvement of protection of the Russian Far East coastal shorebird stopover sites, by providing information to support local and national decision making on key habitat identification and conservation, including consideration of the new Nature Park in Chukotka and prioritising recovery of closed protected area at Moroshechnaya river mouth in Kamchatka.

2.2 (United States): Gather better information on the abundance, distribution and habitat use of Dunlin and Bar-tailed Godwits at spring and fall staging sites in Alaska.

2.3 (China): Enhance protection of Jiangsu Coast ecosystem, especially the Rudong and Dongtai areas for Spoon-billed Sandpiper and other Arctic-breeding shorebirds considering World Heritage Site Nomination requirements.

2.4 (China): Enhance protection of the Luannan Coast especially Nanpu, Tangshan for Red Knot and other Arctic-breeding shorebirds.

2.5 (China): Enhance protection at Yalu Jiang, Liaoning for Bar-tailed Godwit, Dunlin, Great Knot and other Arctic shorebirds.

2.6 (China): Increase knowledge of key staging and wintering Arctic-breeding shorebirds sites in southern China (Guangdong, Guangxi and Fujian provinces) and improve conservation status of these sites.

2.7 (Republic of Korea): Support efforts to reverse declining trends of AMBI priority species (SBS, Great Knot, Dunlin and other) and improve habitat conservation along the flyway through sharing knowledge and international cooperative projects.

2.8 (Republic of Korea): Promote the importance of conserving Korea.

Contribute to the implementation and development of regional flyway initiatives:
7.1 Promote and support the implementation of regional strategies and flyway initiatives
7.2 Encourage/coordinate the development of an American Mid- continental Flyway strategy

Work with partners to increase the number and quality of population estimates of Arctic-breeding waterbirds in the Central and East Asian Flyways

4.1 (All countries): Work with partners such as EAAF Partnership, Wetlands International and other partners to improve population estimates for AMBI priority species by supporting collation of up-to-date information on estimates and trends.

4.2 (All countries): Cooperate with partners such as the EAAF Partnership Waterbird Monitoring Task Force, Wetlands International, BirdLife International and the Global Flyway Network to strengthen monitoring of Arctic-breeding migratory waterbirds along the flyway, particularly in the Yellow Sea and Southeast Asia.

Harvest assessments and mitigation of unsustainable harvest of Arctic birds

2.1 Work with CBird to promote dialogue with authorities for management plans to combine the knowledge of status of hunted species between countries

2.2 Assess the population-level impact of seabird harvest in relation to other stressors

2.3 Conduct/update holistic harvest studies for circumpolar regions of interest using approaches tailored to regional contexts as appropriate

Mitigate effects of over-abundant white geese populations on shorebird habitat

2.1 Implement management actions resulting from study of white geese impacts in Canada (undertaken as part of AMBI Phase 1)

Address environmental pollution issues

4.1 State of knowledge assessment for plastics in wildlife

4.2 Work with Arctic Council countries and Permanent Participants, PAME, and AMAP to begin to address knowledge gaps

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.

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.