The goal of this work was to assess risk of chemical and biological effects
of metals in reacidified, limed water bodies in Norway and Sweden. The ris
k assessment is based on a literature review and evaluations of water chemi
cal data from the 1995 Nordic Lake Survey. Compared to the pre-liming perio
d, it us unlikely that enhanced remobilization of inorganic aluminium (Al)
or other toxic metals (metal bomb hypothesis) from the catchment, the lake
sediment and/or the streambed will occur when limed waters reacidify. Rathe
r, the concentrations in surface waters are expected to be lower than befor
e liming started, because of reduced atmospheric inputs of both strong acid
s and metals as Cd, Hg, Pb, and Zn during the last 10-20 yr. The concentrat
ions in lakes relative to the biological effect levels, as well as the chem
ical properties of the different metals suggest that the potential biologic
al risks associated to reacidification of limed lakes decrease in the order
Al > Cd > Pb. The risks associated with Cr, Cu, Fe, Mn, Ni and Zn are very
low and do not have to be considered except in waters with known concentra
tions larger than the lowest biological risk level. Such waters are very ra
re (<2%). Aluminium is the metal that should be used to set the limit for j
udging the risk of biological damage due to reacidification of limed surfac
e waters.