Atmospheric acidification of catchment-lake ecosystems may provide natural
conditions for the in-lake control of P cycling. This process is based on t
he elevated transport of aluminum from acidified soils and its subsequent p
recipitation in the water body and is described for strongly acidified fore
st lakes, acidified and circumneutral reservoirs, and a moderately acidifie
d alpine lake. In water bodies with episodically or permanently acidified i
nflows a pH gradient develops between lake water and tributaries due to: (i
) neutralization of acidic inflows after mixing with waters with undepleted
carbonate buffering system, and/or (ii) the in-lake alkalinity generation
dominated by biochemical removal of NO3- and SO42- With the pH increasing t
owards neutrality, ionic Al species hydrolyze and form colloidal Al hydroxi
des (Al-part) with large specific surfaces and strong ability to bind ortho
phosphate from the liquid phase. Moreover, Al-part settles and increases th
e P sorption capacity of the sediment. The presence of Al-part on the botto
m reduces orthophosphate release from sediments after its liberation from f
erric oxyhydroxides during anoxia because Al-part is not sensitive to redox
changes. Consequently, the natural in-lake P inactivation may be expected
in any water body with elevated Al input and a pH gradient between its inle
t and outlet. (C) 2001 Elsevier Science Ltd. All rights reserved.