In Norway, a variable pH target (pH 6.2-6.4 during most of the year, but 6.
4 during the smoltification period) is used to reduce the cost of liming sa
lmon rivers. Here we test the adequacy of this liming strategy. Atlantic sa
lmon presmolts exposed to sublethal acidic water (pH 5.9, <25<mu>g Ali.L-1)
for more than 3 months showed impaired seawater tolerance, elevated gill-A
l concentrations, severe gill tissue changes, elevated blood plasma glucose
concentrations, but no effect on blood plasma chloride. It is usually assu
med that smolt will recover from prior aluminum (Al) exposure if water qual
ity is restored. Recovery rate is here used as an indirect measure of water
quality improvements achieved after treating acid water (pH 5.8, 85 mug Al
i.L-1) with lime to reach pH-target levels of 6.0 - 6.3. Fish were exposed
in a channel-tank set-up for >210 hrs in water aged from 1 minute up to 2 h
ours after treatment (in a flow through system). More Al was eliminated fro
m the gills when the fish were exposed to pH 6.3 than to pH 5.8 or 6.0, and
when water was aged after pH increase. Recovery, defined as return of norm
al gill morphology, blood homeostasis and establishment of seawater toleran
ce was achieved within 210 hrs in channels treated with lime to pH 6.3, whi
le a similar recovery was not obvious at lower pH values. Liming to pH 6.3
detoxified Al better than pH 6.1.