Changes in chemical processes in soils caused by acid precipitation

In the absence of SO _infin4 ^sup= and NO _inf3 ^su? in precipitation, the pH of precipitation is primarily a function of CO₂?₂0 equilibria. Soil CO₂ and organic acids, acquired during descent through soil profiles, augment the dissolving capacity of the solutions which initially may have a pH of 4 or lower. The recent man-related increase of H₂SO₄ and HNO₃ in rainfall results in a significant lowering of pH in incident precipitation and an increase in corrosiveness of soil solutions. H₂SO₄ and HNO₃ may contribute some Eh buffering capacity. Particularly susceptible to these changes are clay minerals and redox sensitive elements such as Fe, Mn, Ni, and Co. The overall chemical weathering trends associated with increased acidity of rainfall will be de-stabilization and eventual solution of clay minerals (and the loss of their cation exchange capacity), increased rates of chemical denudation, and solution of illuvial Fe and Al oxides and hydroxides. The latter results in the loss of the adsorbed and coprecipitated metal trace elements associated with these highly reactive phases. The general result in soils developed on non-carbonate substrates is a tendency toward extensive podsolization, with associated decrease in clay minerals, loss of cation exchange capacity, and decrease in fertility.