Weathering and humidity cell tests were used to predict the potential for acid mine drainage (AMD) and to estimate the mineral reaction rates and depletion of fine and coarse tailings from the abandoned Kettara mine, Morocco. The geochemistry of the fine and coarse mine wastes was similar and, as expected by static tests, the wastes produced significant amounts of AMD. The sulfate production rate of both fine and coarse tailings was very high (2,000–8,000 and 2,400–560 mg SO4/kg/week, respectively) during the first weeks of kinetics tests. After 9 weeks, sulfate release became low, ranging between 600 and 78 mg SO4/kg/week for fine tailings and 500–120 mg SO4/kg/week for coarse tailings. Effluent water samples had low pH (2.9–4.2) and elevated concentrations of acidity, sulfate, iron, copper, and zinc. Most or all of the dissolved K, Na, Al, Mg, and Si in the AMD result from the acidic dissolution of silicates (chlorite, talc, muscovite, and albite). Fine tailings produce much higher concentrations of acidity and sulfate than coarse tailings. However, due to greater transport of oxygen and water within the coarse waste, coarse tailings could be of greater environmental significance than fine tailings. The coarse waste continued to release acid after 378 days of leaching, whereas the fine tailings naturally passivates. These laboratory results agree with field observations; the upper profile of the coarse waste rock dam is highly oxidized (75 cm) whereas oxidation in the fine tailings does not extend more than 5–15 cm beneath the surface. A comparison between weathering and humidity cell tests indicated that the general trend of dissolution of metals was essentially similar for both methods. However, sulfate depletion rates were higher for the weathering cell tests. These tests indicate that the Kettara tailings piles and dam will continue to release acid for a long time unless remedial action is taken.
[1]
F. T. Caruccio,et al.
A COMPARATIVE STUDY OF TAILINGS ANALYSIS USING ACID/BASE ACCOUNTING, CELLS, COLUMNS AND SOXHLETS
,
1990
.
[2]
R. W. Lawrence,et al.
Evaluation of Laboratory Kinetic Test Methods for Measuring Rates of Weathering
,
2002
.
[3]
I. González,et al.
Cyclic voltammetry applied to evaluate reactivity in sulfide mining residues
,
2001
.
[4]
M. Aubertin,et al.
A laboratory study of covers made of low-sulphide tailings to prevent acid mine drainage
,
2004
.
[5]
D. Crerar,et al.
Biogeochemistry of acid mine drainage and a method to control acid formation
,
1981
.
[6]
Mati Raudsepp,et al.
Static tests of neutralization potentials of silicate and aluminosilicate minerals
,
2002
.
[7]
M. Benzaazoua,et al.
Acid Mine Drainage at the Abandoned Kettara Mine (Morocco): 1. Environmental Characterization
,
2008
.
[8]
J. Raymund Hoffert,et al.
Acid Mine Drainage
,
1947
.
[9]
G. Furrer,et al.
The coordination chemistry of weathering: I. Dissolution kinetics of δ-Al2O3 and BeO
,
1986
.
[10]
G. M. Ritcey.
Tailings Management: Problems and Solutions in the Mining Industry
,
1989
.
[11]
M. Benzaazoua,et al.
Kinetic tests comparison and interpretation for prediction of the Joutel tailings acid generation potential
,
2004
.
[12]
B. Wehrli.
Monte Carlo simulations of surface morphologies during mineral dissolution
,
1989
.