Jl. Desgranges et al., MERCURY ACCUMULATION AND BIOMAGNIFICATION IN OSPREYS (PANDION HALIAETUS) IN THE JAMES BAY AND HUDSON-BAY REGIONS OF QUEBEC, Archives of environmental contamination and toxicology, 35(2), 1998, pp. 330-341
Mercury exposure was examined in adults and nestlings of ospreys (Pand
ion haliaetus) from lakes, rivers, and hydroelectric reservoirs in nor
thern Quebec between 1989 and 1991 by assessing the amount of mercury
transferred from fish to ospreys, which are voracious fish-eaters. The
high mercury concentrations detected in adult feathers and tissues (f
eathers, blood, liver, kidneys, muscles, brain) of nestlings indicate
an increase in mercury availability at recently constructed hydroelect
ric reservoirs (10-12 years for the La Grande-2 Reservoir). With mean
total mercury levels of 37.3 mg/kg and 1.9 mg/kg in feathers (dry weig
ht) and in blood (wet weight), respectively, contamination rates were,
in both tissues, five times higher for chicks born near the La Grande
Reservoirs (western sector) than in those oared in natural habitats.
Furthermore, the mean quantity of total mercury in 40-day-old chicks r
eared near a reservoir was 10.5 mg, compared with to 1.6 mg for those
reared in a natural environment. Modeling of mercury transfer from fis
h to osprey nestlings showed that the mercury level in chicks' blood p
rovides a good estimate of mercury concentrations in ingested food. In
addition, the relationship between mercury concentrations in the bloo
d and that in feathers indicates that substantial biomagnification of
mercury occurs from the ingested dose to the feathers. The intensity o
f this biomagnification varies with the age of the chicks and reaches
a maximum value as the flight feathers start to form (at 20-25 days of
age) declining thereafter until the bird is 45 days old and growth of
those feathers is complete. Nevertheless, the mean number of young fl
edged on reservoirs where mercury exposure is greatest (>40 mg/kg of H
g in chicks' feathers) did not differ (1.6 +/- 0.7) from that observed
elsewhere in built-up environments (1.9 +/- 0.7) or in natural habita
ts (2.0 +/- 0.7) (H = 4.39; p = 0.11). Storage of mercury in growing f
eathers (86% of all mercury in osprey) prevents accumulation in living
tissues, thereby protecting the chick from related toxic effects. How
ever, toxicological problems may arise after fledging. In particular,
attention should be paid to postfledging survival before concluding th
at mercury exposure is insufficiently high in Osprey young reared at r
eservoirs.