Hydrochemical data have been collected for between 6 and 9 years from
forest harvesting experiments in small catchments (>10 ha) at Plynlimo
n and Beddgelert, Wales, UK. Felling resulted in rapid increases in NO
3- and K+ concentrations at both sites. A maximum of 3.2 mg N L(-1) wa
s observed at Plynlimon about one year after the start of felling. Con
centrations declined to control stream values (0.5 mg N L(-1)) after 5
years. At Beddgelert, NO3- concentrations in the manipulated catchmen
ts remained above those in the unfelled control catchment for three ye
ars, before declining below control values. The NO3- pulse was related
to increased rates of mineralization acid nitrification in the soil a
fter felling. The initial increase in K+ concentration after felling a
t Plynlimon was followed by a slow decline, but concentrations were st
ill above those in the control stream after 5 years. From 4 to 8 years
after felling at Beddgelert, K+ concentrations fell below and then ge
nerally remained lower than control values. The NO3- pulse after felli
ng at Plynlimon sustained inorganic anion concentrations above those i
n the control stream for the first 18 months after felling. As the NO3
- pulse declined, inorganic anion concentrations decreased to below th
ose in the control stream about 4 years after felling. At Beddgelert,
the smaller increase in NO3- concentrations had less of an effect on i
norganic anion concentrations which decreased after felling relative t
o values in the control stream. The increase in NO3- was associated wi
th temporary streamwater acidification in the felled catchments due to
the increased rates of nitrification and nitrate leaching. At Plynlim
on, streamwater filterable Al concentrations declined after felling, b
ut controls on Al behaviour are complex and not explained by simple eq
uilibrium relationships with Al(OH)(3) or by variations in inorganic a
nion concentrations. At Beddgelert, felling had no effect on stream wa
ter filterable Al concentrations. Felling at Plynlimon led to a large
reduction in streamwater Cl-, Na+ and SO42- concentrations. At Beddgel
ert reductions in SO42- and 'sea salt' ion concentrations were less cl
ear, reflecting the smaller proportions of the catchments which were h
arvested. Felling had no deleterious effects on water quality, apart f
rom a temporary slight further decline in stream pH at Beddgelert. Inc
reases in NO3- concentrations were short-lived and concentrations were
well below drinking water standards. Filterable Al concentrations wer
e already higher than statutory standards, but were not increased or d
ecreased through felling.