S. Peiffer et al., IMPACT OF HIGH ALUMINUM LOADING ON A SMALL CATCHMENT-AREA (THURINGIA SLATE MINING AREA) GEOCHEMICAL TRANSFORMATIONS AND HYDROLOGICAL TRANSPORT, Water, air and soil pollution, 94(3-4), 1997, pp. 401-416
A field study was performed on the effects of acid mine leachate from
slate mine tailings seeping into a small river passing through the tai
lings. Before entering the tailings the river water has high alkalinit
y which neutralizes acidity upon mixing with leachate within the taili
ngs. Downstreams of the tailings the pH of the river water ranges abou
t pH = 8, the water contains high concentrations of sulfate (approxima
te to 1500 mu mol/l) and particulate bound aluminium (approximate to 8
0 mu mol/l), but low concentrations of dissolved aluminium (approximat
e to 3 mu mol/l). It is therefore assumed that Al(OH)(3) colloids are
precipitated during the neutralisation process and transported out of
the tailings. The concentration of particulate bound aluminium along t
he river shows a strong correlation with the concentration of sulfate,
which indicates that particulate bound aluminium is conservative. It
therefore seems that under dry weather conditions (under most of the s
ampling was performed) no chemical retention mechanism exists which co
nfines the distribution of aluminium to a restricted part of the catch
ment area. In contrast, the white river sediment is rich in both alumi
nium and sulfate, which suggests the temporary formation of aluminium
hydroxosulfate minerals. Favorable (i.e. acidic) conditions may prevai
l at high discharges where the acidity accumulated in the tailings is
flushed into the river with its subsequent acidification.