Je. Lagerquist et al., LEAD-POISONING AND OTHER CAUSES OF MORTALITY IN TRUMPETER (CYGNUS BUCCINATOR) AND TUNDRA (C-COLUMBIANUS) SWANS IN WESTERN WASHINGTON, Journal of wildlife diseases, 30(1), 1994, pp. 60-64
Lead poisoning and other causes of mortality of 115 trumpeter (Cygnus
buccinator) and 21 tundra (C. columbianus) swans from northwestern Was
hington (USA) from 1986 to 1992 are reported. Necropsies were performe
d on all 136 swans, liver lead analysis conducted on 110, and differen
tiation between lead and steel shot pellets recovered from gizzards in
97 swans. Shot pellets were detected in 44 (32%) of 136 gizzards. Lea
d shot was recovered from 32 (33%) of 97 gizzards and steel shot from
16 (16%). Mean intensity of lead shot in gizzards was nearly five time
s greater than steel shot. Thirty-nine (35%) of 110 livers had lead co
ncentrations diagnostic of lead poisoning(>6 ppm, wet weight). Mean (/-SE) weight for 61 non-bad poisoned trumpeter swans was 9.8 (+/-0.30)
kg, significantly heavier (P < 0.05) than 30 lead poisoned trumpeters
(($) over bar x = 6.8 +/- 0.23 kg). There was no significant differen
ce (P > 0.05) in weights between lead poisoned (n = 9) and non-lead po
isoned (n = 12) tundra swans. Lead poisoning was the primary cause of
death, accounting for 29% of the mortalities. Other causes of mortalit
y identified were aspergillosis (17%), illegally shot (11%), and other
traumatic factors (12%). The cause of death for 43 swans was not dete
rmined. Lead poisoning from the ingestion of lead shot continues to be
a principal cause of mortality in swans overwintering in northwestern
Washington.