This study examines the removal of dissolved metals during the oxidation and neutralization of five acid mine drainage (AMD) waters from La Zarza, Lomero, Esperanza, Corta Atalaya and Poderosa mines ( Iberian Pyrite Belt, Huelva, Spain). These waters were selected to cover the spectrum of pH (2.2 - 3.5) and chemical composition ( e. g., 319 - 2,103 mg/L Fe; 2.85 - 33.3 g/L SO4=) of the IPB mine waters. The experiments were conducted in the laboratory to simulate the geochemical evolution previously recognized in the field. This evolution includes two stages: ( 1) oxidation of dissolved Fe(II) followed by hydrolysis and precipitation of Fe(III), and ( 2) progressive pH increase during mixing with fresh waters. Fe( III) precipitates at pH < 3.5 ( stages 1 and 2) in the form of schwertmannite, whereas Al precipitates during stage 2 at pH 5.0 in the form of several hydroxysulphates of variable composition (hydrobasaluminite, basaluminite, aluminite). During these stages, trace elements are totally or partially sorbed and/or coprecipitated at different rates depending basically on pH, as well as on the activity of the SO 4 anion ( which determines the speciation of metals). The general trend for the metals which are chiefly present as aqueous free cations (Pb2+, Zn2+, Cu2+, Cd2+, Mn2+, Co2+, Ni2+) is a progressive sorption at increasing pH. On the other hand, As and V ( mainly present as anionic species) are completely scavenged during the oxidation stage at pH < 3.5. In waters with high activities (> 10(-1)) of the SO4- ion, some elements like Al, Zn, Cd, Pb and U can also form anionic bisulphate complexes and be significantly sorbed at pH < 5. The removal rates at pH 7.0 range from around 100% for As, V, Cu and U, and 60 - 80% for Pb, to less than 20% for Zn, Co, Ni and Mn. These processes of metal removal represent a signi. cant mechanism of natural attenuation in the IPB.