Impoundment is among the most common hydrologic alterations
with
impacts on aquatic ecosystems that can include effects on mercury
(Hg) cycling. However, landscape-scale differences in Hg bioaccumulation
between reservoirs and other habitats are not well characterized nor
are the processes driving these differences. We examined total Hg
(THg) concentrations of Smallmouth Bass (
Micropterus
dolomieu
) collected from reservoir, tailrace, and
free-flowing reaches along an 863 km segment of the Snake River, USA,
a semiarid river with 22 impoundments along its course. Across three
size-classes (putative 1-year-old, first reproductive, and harvestable
sized fish), THg concentrations in reservoirs and tailraces averaged
76% higher than those in free-flowing segments. Among reservoirs,
THg concentrations were highest in reservoirs with inconsistent stratification
patterns, 47% higher than annually stratified, and 144% higher than
unstratified reservoirs. Fish THg concentrations in tailraces immediately
downstream of stratified reservoirs were higher than those below unstratified
(38–130%) or inconsistently stratified (32–79%) reservoirs.
Stratification regimes influenced the exceedance of fish and human
health benchmarks, with 52–80% of fish from stratifying reservoirs
and downstream tailraces exceeding a human consumption benchmark,
compared to 6–17% where stratification did not occur. These
findings suggest that impoundment and stratification play important
roles in determining the patterns of Hg exposure risk across the landscape.