An experimental short-term acidification with HCl at a first-order stream i
n central Maine, USA was used to study processes controlling the changes in
stream chemistry and to assess the ability of stream substrate to buffer p
H. The streambed exerted a strong buffering capacity against pH change by i
on exchange during the 6-hour acidification. Streambed substrates had subst
antial cation and anion exchange capacity in the pH range of 4.1 to 6.5. Th
e ion exchange for cations and SO42- were rapid and reversible. The speed o
f release of cations from stream substrates was Na1+ > Ca2+ > Mg2+ > Aln+ >
Be2+, perhaps relating to charge density of these cations. Ca2+ desorption
dominated neutralisation of excess H+ for the first 2 hr. As the reservoir
of exchangeable Ca diminished, desorption land possibly dissolution) of Al
3+ became the dominant neutralising mechanism. The exchangeable land possib
ly soluble) reservoir of Al was not depleted during the 6-hour acidificatio
n. Sulphate adsorption during the acidification reduced the concentration o
f SO42- in stream water by as much as 20 mu eq L-1 (from 70 mu eq L-1). Des
orption of SO42- and adsorption of base cat ions after the artificial acidi
fication resulted in a prolongation of the pH depression. The streambed had
the capacity to buffer stream water chemistry significantly during an acid
ifying event affecting the entire upstream catchment.