Laboratory
Study of Particle Resuspension, Oxidation and Metal Release in
Flooded Mine Tailings
Mine Environment Neutral Drainage at CANMET-MMSL |
Rapport
NEDEM 2.15.3
November 1998
EXECUTIVE
SUMMARY
The
use of shallow water cover (up to 2 m) to flood reactive sulphide
mine tailings is a popular method of acid drainage prevention used
by the mining industry. In flooded tailings, wind-induced turbulence
can increase the oxygen flux from air into water by creating turbulence
at the air-water interface, thus promoting mechanical mixing of
oxygen from air into the water and thus keeping the dissolved oxygen
concentrations at saturation levels. Turbulence can also resuspend
tailings particles in the oxygen-saturated water cover and expose
tailings to greater contact with oxygen, possibly leading to increased
oxidation and metal release.
In
late 1996, the Geotechnical Research Centre at The University of
Western Ontario initiated a study to investigate the contribution
of resuspension to tailings oxidation and acid generation under
laboratory conditions. The study was undertaken on behalf of MEND
and sponsored by Battle Mountain Canada Limited, Falconbridge Limited,
INCO Limited, Noranda Mineral and Exploration Limited, Teck Corporation,
Ontario Ministry of Northern Development and Mines and Canada Centre
for Mineral and Energy Technology (CANMET) through the CANADA/Northern
Ontario Development Agreement (NODA). This report presents the results
of the study.
The
study involved a series of laboratory experiments performed in Plexiglas
columns packed with unoxidized pyrrhotite tailings, which were then
flooded with 45, 60 and 80 cm deep water covers. The tailings were
obtained directly from the mill discharge pipelines at the Falconbridge
Strathcona Mines, near Sudbury, Ontario. The water cover was stirred
at 140, 170 and 200 revolutions per minute to suspend the underlying
tailings. Control experiments involving water-covered tailings without
stirring were also conducted for comparison. To facilitate the analysis
of the results, the stirrer speed and the depth of water cover were
used to define a mixing index, a dimensionless parameter that measures
the degree of mixing in the water cover. Oxygen mass transfer from
air to the water cover was measured for each mixing index. The water
cover was also monitored for dissolved oxygen (DO), pH, conductivity,
sulphate and metals. At the end of the experiments (126 days), suspended
tailings, surficial tailings and undisturbed solid tailings and
pore water were sampled for chemical analysis. The bulk and surface
mineralogy of the tailings was also examined.
Key findings
and conclusions arising from the study are as follow:
- Resuspension
increases sulphide tailings oxidation, acid generation and metal
release. This is based on sulphide (pyrrhotite) depletion, oxygen
consumption, pH, sulphate and metal loadings.
- Oxidation
products are lighter than the original tailings (specific gravity
of 2.7 versus 3.9-4.4 for the original tailings).
- Oxidation
products include iron oxyhydroxides (possibly goethite) and gypsum.
- Suspended
tailings are finer than tailings at rest: 80% of the suspended
tailings are finer than 0.018 mm, compared to only 30% of the
original tailings.
- Unoxidized
suspended tailings contain sulphide mineral (pyrrhotite) as well
as gangue minerals.
- The rate
at which oxygen is transferred into the water cover is independent
of mixing index.
- The release
of nickel, zinc, aluminium, and manganese increases with mixing
index.
8. Significant
bed erosion occurs at a threshold (critical) mixing index. This
threshold value would occur in shallow water covers (possibly
60 cm or shallower).
The
results of the study suggest that when tailings are resuspended,
whether by mechanical stirring or by intense wind and wave activity,
sulphide oxidation is accelerated with consequent precipitation
of secondary iron oxyhydroxide minerals. These minerals tend to
have a large surface area when freshly precipitated and can adsorb
or scavenge trace metals released during the primary oxidation reactions.
Further research is recommended to assess the long-term stability
of the oxyhydroxides, especially as conditions in the water become
reducing, under which iron hydroxides tend to dissolve and are likely
to release scavenged metals. Metals released in the water cover,
as a result of increased oxidation due to resuspension, do not infiltrate
deep into the underlying tailings. The impact of this resuspension-induced
oxidation and metal release on the overall water quality in the
field should be assessed. Various factors including dilution and
contributions from groundwater and precipitation will have an influence
on the overall water quality in the field. These factors are not
evaluated in the present laboratory study.
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