As atmospheric emissions of S have declined in the Northern Hemisphere, the
re has been an expectation of increased pH and alkalinity in streams believ
ed to have been acidified by excess S and N. Many streams and lakes have no
t recovered. Evidence from East Bear Brook in Maine, USA and modelling with
the groundwater acid-base model MAGIC (Cosby et al. 1985a,b) indicate that
seasonal and yearly variations in soil PCO2 are adequate to enhance or eve
n reverse acid-base (alkalinity) changes anticipated from modest decreases
of SO4 in surface waters. Alkalinity is generated in the soil by exchange o
f H+ from dissociation of H2CO3, which in turn is derived from the dissolvi
ng of soil CO2. The variation in soil PCO2 produces an alkalinity variation
of up to 15 mu eq L-1 in stream water. Detecting and relating increases in
alkalinity to decreases in stream SO4 are significantly more difficult in
the short term because of this effect. For example, modelled alkalinity rec
overy at Bear Brook due to a decline of 20 mu eq SO4 L-1 in soil solution i
s compensated by a decline from 0.4 to 0.2% for soil air PCO2. This compens
ation ability decays over time as base saturation declines. Variable PCO2 h
as less effect in more acidic soils. Short-term decreases of PCO2 below the
long-term average value produce short-term decreases in alkalinity, wherea
s short-term increases in PCO2 produce shortterm alkalization. Trend analys
is for detecting recovery of streams and lakes from acidification after red
uced atmospheric emissions will require a longer monitoring period for stat
istical significance than previously appreciated.