The widespread recent decline in the species diversity and population
density of freshwater mussels in North America may be partly related t
o chronic, low-level exposure to toxic metals. As benthic filter-feedi
ng organisms, freshwater mussels are exposed to metals that are dissol
ved in water, associated with suspended particles and deposited in bot
tom sediments. Thus, freshwater mussels can bioaccumulate certain meta
ls to concentrations that greatly exceed those dissolved in water. In
adult mussels, the most common site of metal uptake is the gill, follo
wed by the mantle and the kidney. The toxic effects of metals on fresh
water mussels have been examined in a few acute toxicity tests, but th
e sublethal effects of long-term exposure to low environmental concent
rations are little understood. Sublethal exposure to metals can alter
growth, filtration efficiency, enzyme activity and behaviour. Subletha
l effects are frequently observed at concentrations that are only half
the lethal concentrations. However, few toxicity tests have used envi
ronmentally realistic exposure concentrations. Total concentrations of
Cd, Cu, Hg and Zn in many oxic surface waters are in the ngl(-1) rang
e, yet many toxicity studies have exposed mussels to concentrations in
the mu gl(-1) or even the mgl(-1) range. An understanding of the proc
esses by which metals affect freshwater mussels would provide insights
on the ecotoxicological significance of metal contamination to natura
l mussel populations and aid in the development of water-quality crite
ria that adequately protect mussels.