6.6. RECOVERY OF METALS FROM WASTES 539
Separation by Magnus-Robins Eect
It was demonstrated by Robins and later by Magnus that a particle, rotating
either in water or air, does not fall strictly vertically, but, as a result of asymme-
try of the flow and pressures around the rotating particle, a lift force is created
that aects the particle trajectory [M45, B51, T13].
It has been suggested by Rem et al. [F36] that this eect can be applied to
the separation of fine non-ferrous metal particles from a mixture. By exposing
a mixture of vertically falling particles to a rotating magnetic field, the non-
ferrous metal particles, in contrast to non-metallic particles, also start rotating.
The Magnus lift force thus created deflects the metal particles from the vertical
direction, as shown in Fig. 6.59.
A wet Magnus separator was applied, on pilot scale, to the separation of
copper and aluminium particles from the bottom ash of a municipal waste in-
cinerator [F36]. A production-size plant with a throughput of 50 t/h has been
proposed [R31]. The wet Magnus separator can treat particles in the size range
from 0.5 to 20 mm, while in a dry mode the size range is from 0.2 to 5 mm.
6.6.2 Sorting of heavy non-ferrous metals
Heavy non-ferrous metals include copper, lead, zinc, titanium, cobalt and pre-
cious metals such as silver, gold and platinum, and metal alloys such as brass
(Cu+Zn) and bronze (Cu+Sn+Zn). Approximately 75% of the mixture of heavy
non-ferrous metals comes from automobile scrap, the source of the rest being
electronic and domestic waste. Brass and copper make up approximately 70%
of the value of the mixture, as is illustrated in Fig. 6.60.
Hand sorting is generally the most cost-eective method for sorting of heavy
metals. Labour rates for sorting in Asia are low and the costs of shipping scrap
materials, from most parts of the world, to Asia are presently very attractive.
Moreover, the Asian markets for non-ferrous metals are more attractive than,
for instance, the European markets.
A rather recent entry into the sorting of heavy non-ferrous metals is colour
sorting. High-speed, real-time processors interpret images from high-resolution
cameras. The processors are pre-programmed to recognize certain metals by
colour and geometry and compressed air is used to eject the recognized metal
fragments. One metal type can be recovered per cycle per unit. The e!ciency of
this technique is limited by, for instance, insu!cient liberation, contamination,
dirt and corrosion. Recovery ranges from 80% for lead to 93% for zinc, while
the purity of the concentrates is approximately 95% to 98%.
Sorting in a magnetic fluid
Separation in magnetic fluids, and particularly in ferrofluids (FHS) is a natural
choice for sorting of non-ferrous metals into individual metal concentrates. Con-
siderable eort was expended to develop the FHS for the treatment of automo-
bile scrap [K16, K17, F21, S50, N4, R9, H35, A44], followed by the application