Lead shot ingestion is the primary source of elevated lead exposure an
d poisoning in waterfowl and most other bird species. For some species
(e.g. Common Loons, Gavia immer), lead sinker ingestion is a more fre
quent cause of lead poisoning. In freshwater environments where recrea
tional angling activity and loon populations co-occur, lead poisoning
from ingestion of small (< 50 gram) lead sinkers or jigs accounts for
10-50% of recorded adult loon mortality, depending on the locations st
udied. Lead shot ingestion occurs in waterfowl, and in a wide variety
of non-waterfowl species, including upland game birds, shorebirds, rap
tors, and scavengers. Where it has been explicitly studied in Canada a
nd the US, lead poisoning mortality of bald (Haliacetus leucocephalus)
and golden eagles (Aquila chrysactos) from eating prey animals with l
ead shot embedded in their Tissues accounts for an estimated 10-15% of
the recorded post-fledging mortality in these raptorial species. In a
ddition to environments that experience hunting with lead shot, clay t
arget shooting ranges, especially those in which the shotfall zones in
clude ponds, marshes, lakes, dyers, beaches, or other aquatic-type env
ironments, create a significant risk of shot ingestion and poisoning f
or waterbirds. Metallic lead pellets deposited onto soils and aquatic
sediments are not chemically or environmentally inert, although tens o
r hundreds of years may be required for total breakdown and dissolutio
n of pellets. Functional, affordable non-toxic alternatives to lead sh
ot and sinkers are being currently produced, and additional such produ
cts are being developed. Several countries have successfully banned th
e use of small lead sinkers, and of lead shot for waterfowl and other
hunting, also for clay target shooting, using a phasing-out process th
at gives manufacturers, sellers, and users adequate time to adjust to
the regulations.