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A. Status of the Spectacled Eider - U.S. Fish and Wildlife Service

A. Status of the Spectacled Eider - U.S. Fish and Wildlife Service

A. Status of the Spectacled Eider - U.S. Fish and Wildlife Service

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surface after a year <strong>and</strong> is no longer available to foraging ducks. Because soil dynamics are<br />

different in sub-arctic <strong>and</strong> arctic wetl<strong>and</strong>s, <strong>the</strong> long-term behavior <strong>of</strong>lead shot at higher latitudes<br />

is not known. Controlled, site-specific studies <strong>of</strong>multi-year lead shot behavior should be<br />

conducted in principal substrates found in arctic <strong>and</strong> sub-arctic wetl<strong>and</strong>s used by foraging<br />

<strong>Spectacled</strong> <strong>Eider</strong>s.<br />

D6. 1. Investigate lead shot persistence <strong>and</strong> availability on <strong>the</strong> YKD. This task was initiated<br />

in 1994.<br />

D6.2. Investigate lead shot persistence <strong>and</strong> availability on <strong>the</strong> NS This task will only be<br />

needed ifeider screening (task D4.2) indicates a problem with lead exposure on <strong>the</strong> NS. A<br />

study <strong>of</strong>lead shot persistence on <strong>the</strong> NS potentially would illuminate concerns for both NS<br />

<strong>and</strong> AR nesting populations, since wetl<strong>and</strong> soils at similar latitudes might be similar.<br />

D7. Determine contaminant sources. transport modes. <strong>and</strong> uptake mechanisms. If<br />

contaminants are determined .to be a factor affecting <strong>Spectacled</strong> <strong>Eider</strong>s (tasks C5. 1 <strong>and</strong> Dl),<br />

studies should be initiated to trace contaminants to <strong>the</strong>ir source(s) (also see task D3).<br />

D8. Design <strong>and</strong> implement a monitoring program to assess contaminant levels in each<br />

population over time. Ifcontaminants are determined to be adversely affecting <strong>Spectacled</strong> <strong>Eider</strong>s<br />

(tasks Dl <strong>and</strong> CS. 1), a long-term monitoring program should be implemented.<br />

E. ERilahlila<br />

El. Assess eider diets in marine habitats used during summer, molting. fall staging. winter, <strong>and</strong><br />

~pring..~iaging. Knowledge <strong>of</strong>eider diets is necessary to underst<strong>and</strong> potential obstacles to<br />

recovery such as contaminants <strong>and</strong> competition.<br />

El. 1. Assess food habits from incidentally obtained data. Collecting adequate sample sizes<br />

for a traditional food habits study (i.e., shooting tens <strong>of</strong>birds or more), may not be an<br />

acceptable approach for a threatened species. Thus, food habits information should first be<br />

ga<strong>the</strong>red incidentally from dead birds <strong>and</strong> birds collected for o<strong>the</strong>r purposes (ongoing).<br />

El.2. Develop means <strong>of</strong>capturing live <strong>Spectacled</strong> <strong>Eider</strong>s for marine diet sampling. Task<br />

El. 1 may not result in adequate information about food habits. Iffood habits could be<br />

determined without killing birds, <strong>the</strong>n more accurate information about diet would be possible<br />

without adverse effects on <strong>the</strong> population. Techniques for capturing live eiders at-sea should<br />

be developed.<br />

El.3. Determine food habits in marine environments. Stomach samples should be obtained<br />

by methods developed in task El .2, iffeasible. Ifmethods for capturing live eiders at-sea<br />

cannot be developed, <strong>the</strong>n <strong>the</strong> population effects <strong>of</strong>collecting a valid sample <strong>of</strong>wild birds<br />

should be determined (see task C5.7). If<strong>the</strong>se population effects would not threaten any <strong>of</strong><br />

<strong>the</strong> populations, <strong>the</strong>n collections should be implemented to assess eider diets in marine<br />

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