Ecology
Medvedeva N.P., PhD in Economics, Filippov P.A.,
PhD in Technical Sciences
Novosibirsk state technical university, Russia
Institute of Mining, Siberian Branch, Russian Academy of Sciences, Russia
On timeliness of technogenic
raw materials processing
ANNOTATION: In Siberia about 200 Mt of wastes of the iron ore dressing
processes are stockpiled and occupy the area of more than 100000 m2.
Technogenic formations of aged mine wastes and tailings contain ferrous,
non-ferrous and noble metals (Fe, Co, Zn, Au, and Ag). The modern
mineral-dressing processes allow the efficient processing of available dump
materials to produce marketable products: iron-ore concentrate, base gold,
sulfide concentrates and construction materials.
For the last millennium on the
territory of the Russian Federation more than 60 billion t of industrial wastes
has been stockpiled. These wastes were located on the soil surface as dumps
resulting from operating mines, smelters, heat power stations and other works.
The largest part of the wastes (up to 90%) is the mining industry wastes. In
the Siberian region about 800 million t of the tailings are produced by mining
and processing and every year they are increased by 18-20 million t.
The intensive mining activity is followed by an ecological
effect of mining on the local environment. The materials sector accounts for
more than 40% of disturbed lands, 30% of harmful atmospheric emissions, and up
to 20% of sewage water release into natural water basins in Russia. The
Kuznetsk Basin, one of the leading metal, coal, ferrous, and non-ferrous
producers in Russia, bears the heaviest ecological load.
The West Siberian
metallurgical complex is supplied with local raw materials by six mines with
underground (4) and open cut (2) methods of mining. The mined ore is processed
at crushing and preparation plants to produce the marketable product and
tailings. At the moment about 200 million t of tailings (technogenic
formations) are stockpiled in dumps occupying the territory of more than 500
thousand m2. A part of them is
hazardous and must be isolated, another part contains useful elements and can
be a subject to processing.
The presence of sulfide minerals in the iron ore wastes contributes to
the intensive development of oxidation processes which causes the release of
gold, nickel and other metals from the crystal lattice. The same oxidation processes cause the
formation of ecologically hazardous compounds of sulfur, arsenic and other
elements which negatively affect the biological environment. Arsenic and hazard
category 1 zinc exceed the allowable heavy metal concentration level in the
mining wastes significantly (3-5 times), as well as copper and hazard category
2 cobalt (2-3 times). By the toxicity index the dumps are referred to class IV,
by the value of the total pollution index they are ranked as high and medium
degree of pollution. The technogenic formations contain many useful elements
(Fe, Co, Au, and others) which are of commercial interest for the secondary raw
materials processing from the mining wastes.
The researches [1-3] state that the usage of technogenic mineral
materials at the mining objects is rather cost-effective and by its economical
parameters comparable to the processing of natural resources extracted from
mining of natural (geogenic) deposits. The commercial value of technogenic
formations is sure to account for the ecological component, the preventable
damage to the environment caused by the release of hazardous components and
their compounds to the water basins and emissions into the atmosphere from the
dumps. To process the technogenic formations of Siberian mines an innovative
technology of iron-ore waste dumps is developed [4, 5].
The technology provides placing a mobile modular complex on the dumps
territory (Fig.) to process the wastes for the production of iron-ore
concentrate and fractioned construction materials.
Fig. Technological flowsheet of the modular complex for waste processing
The modular complex consists of a receiving bin, two separators, a
screen and belt conveyors to transport the concentrate. The primary material is
unloaded to the receiving bin by excavator, bulldozer or scraper facilities
It is planned to invest US$ 1,500,000 into construction, assembly works
and purchase of mineral dressing equipment. With the expected annual seasonal
processing rate of 1 million t of wastes at one of the mines it is possible to
obtain 400 thousand t of construction crushed stone and 250 thousand t of
iron-ore concentrate correspondingly. The production cost of the concentrate is
US$ 5.5 per 1 tonne. The project payback period is one year.
The waste processing within the minetake of Sheregeshsky mine solely
will restore more than 50 hectares of reclamated lands for the economy.
The technical result ensures higher efficiency, more complete recovery
of valuable components, and less ecological impact, thanks to the optimal
operating modes of magnetic separation of iron-ore tailings, heterogeneous in
granulometric composition and content of valuable components. In the new
millennium the science can and must suggest the mankind new “green”
technologies of consumer goods production.
References:
1.
Filippov, P. A. 2008. Potentials of technogenic formations
in mines of West Siberia. Journal of Mining Science,
No. 4, 2008, pp.71-77
2.
Filippov,
P.A., Neverov, S.A., Freidin, A.M., Gaidin, A.P. 2009. Technogenic formations
of Siberian mines as the most important source of secondary raw minerals. Proceedings of the Conference in partnership with the foreign scientist
«Fundamental Problems of the Technogenic Geomedium Formation». Two Volumes.
Vol. I. Novosibirsk: Institute of Mining, Siberian
Branch, Russian Academy of Sciences, pp.
536-539.
3.
Freidina,
E.V., Medvedeva, N.P., Filippov, P.A. 2010. Opportunities and assessment of
diversification for mining companies. Proceedings of
the Conference in partnership with the foreign scientist «Fundamental Problems
of the Technogenic Geomedium Formation». – Three Volumes. Vol. II. -
Novosibirsk: Institute of Mining, Siberian Branch, Russian Academy of Sciences, pp. 141-147.
4.
Freidin, A. M, Filippov, P. A. and
Gaidin, A. P., 2002. Process for treatment of iron-ore bearing wastes. Patent
of the Russian Federation 2190027, publ in Bull Inv No27.
5.
Filippov, P.A., 2009. Recycling of iron ore tailings in Siberia
as part of the regional eco-policy and higher sustainability. Innovations. St. Petersbourg, pp. 84-87.