liquefaction) do not apply to this design. The lack of dam walls reduces the possibility of slope failure, but
the stability of the pit slopes do have to be checked.
Unless the purpose is to isolate sulfide tailings underneath water, the water table should be below the tailings
disposed in the pit. This may require backfilling with mine rock or overburden. If backfilling underneath the
tailings is necessary, and/or if the surrounding rock is not sufficiently impermeable, a liner may be required.
Ritcey (1989) notes that the hydrogeological parameters affecting the migration of seepage and contaminants
are poorly understood, so tailings with toxic contaminants or reactive tailings may be poor candidates for this
type of impoundment.
When mining in an active pit is proceeding laterally, the mined-out portion of the pit may be suitable for
tailings disposal. In such cases, dikes would be constructed to impound the tailings in the mined-out area.
This embankment could then be raised in a phased approach (Ritcey 1989).
2.2.4Specially Dug Pit Impoundment Design
This design is fairly unusual and involves the excavation of a pit specifically for the purpose of tailings
disposal. The impoundment consists of four or more cells with impermeable liners and surrounded by an
abovegrade dam. Material removed from the pit is used in construction of the dam. This dug pit/dam design
has some of the same advantages as the ring-dike design, including site independence and uniform shape.
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