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
Geoecological and economic
evaluation of technogenic mineral formation of mines in Siberia
ANNOTATION: The problems of mine dumps maintenance and problems of development
of technogenic mineral formations that contain ferrous, non-ferrous, rare,
precious metals and that are interesting as a source of processed raw materials
for Ore Mining and Processing Industrial Complexes are covered.
Mining, processing and development of mineral resources is inevitably
followed by the formation of a significant volume of the mined and processed
waste material. Thus mines and iron ore processing plants in Siberia possess
voluminous dumps of waste materials (technogenic formations) that occupy huge
areas. These dumps accumulate useful and toxic elements [1]. The content of
iron in some dumps often exceeds the content of iron in the mined ores to be
processed. This is in particular true for the old dumps which had been formed
in the first half of the previous century when a complex study of mineral resources was not taken into due consideration and the
treatment of iron ore deposits used to derive only one element - Fe. More than 50% of iron was left in the
wastes from processing plants, some other useful minerals were lost in waste
products as well. So far the iron ore
dumps of the Siberian region on the territory of more than 500 th. m2
have accumulated about 200 mln. t. of tails (table 1). A part of them is
hazardous and needs to be isolated, another part contains useful elements and should be
retreated.
Table 1.
Tails of ore processing
in mine dumps
|
Company name |
Quantity, mln.t. |
Area, ha |
Useful elements |
|
Mines
|
||||
|
Sheregeshsky |
23,2 |
50,9 |
Fe, Mn, Zn, Au |
|
|
Kazsky |
7,2 |
6,3 |
Cu,
Zn, Au |
|
|
Tashtagolsky |
0,3 |
0,2 |
Fe |
|
|
Abakansky |
20,1 |
28,0 |
Co, Cu, Ni |
|
|
Teysky |
21,2 |
19,l |
Co,
Zn |
|
|
Irbinsky |
6,7 |
4,7 |
Co, Cu, Zn |
|
Processing
plants
|
||||
|
Mundibashskaya |
30,1 |
60,1 |
Au, Ag, Zn |
|
|
Abagurskaya |
89,1 |
385,2 |
Zn, Cr, Co |
|
|
Total |
198,1 |
554,3 |
- |
|
The natural wind erosion of mine dumps provokes
venting into the air of a large amount of dust which pollutes agricultural and
forestry areas. The presence of sulphide minerals in mine tails contributes to
the intense development of oxidation processes which result in the release of
gold, nickel and other metals from a crystalline lattice. The same oxidation
processes result in the formation of environmentally hazardous compounds of
sulphur, arsenic and other elements which negatively affect the biological
environment [2]. The content of
chemical elements in the dumps and soils of the Teysky mine is given in table
2.
Table 2.
Content
of chemical elements (mg/kg) in mine wastes and their allowable concentrations
|
Element |
Name of dump |
Maximum allowable
concentration for soils |
Approxible allowable
concentration for soils |
|
||
|
Severny |
Juzhny |
Shlamovy |
||||
|
I substance hazard
category |
||||||
|
As |
7,9 |
17,3 |
37,4 |
|
5,0 |
1,7 |
|
Cd |
0,3 |
0,21 |
0,495 |
|
1,0 |
0,13 |
|
Hg |
0,03 |
0,03 |
0,03 |
2,1 |
|
0,083 |
|
Zn |
382,9 |
41,8 |
62,0 |
|
110,0 |
83,0 |
|
II substance hazard
category |
||||||
|
B |
54,3 |
86,4 |
192,0 |
|
|
12,0 |
|
Co |
3,2 |
7,0 |
46,8 |
|
12,0 |
18,0 |
|
Ni |
16,7 |
14,4 |
27,0 |
|
40,0 |
58,0 |
|
Cr |
75,9 |
35,7 |
76 |
|
|
83,0 |
|
Cu |
874,4 |
392,3 |
63,9 |
|
66,0 |
47,0 |
|
Mo |
2,0 |
2,3 |
30,0 |
|
|
1,1 |
|
III substance hazard
category |
||||||
|
Ba |
24,6 |
49,8 |
138,0 |
|
|
650,0 |
|
V |
53,3 |
50,0 |
82,5 |
150,0 |
|
90,0 |
|
Mn |
448,0 |
674,0 |
938,0 |
1500,0 |
|
1000,0 |
|
Sr |
98,1 |
121,7 |
48,9 |
|
|
3430,0 |
|
Radioactive elements |
||||||
|
U |
5,8 |
7,4 |
19,0 |
|
|
2,5 |
|
Th |
3,2 |
1,3 |
2,7 |
|
|
13,0 |
Arcenic and zink
both having the first substance hazard category as well as copper and cobalt
(the second hazard category) significantly exceed the approxible allowable
concentration of heavy metals in mine dumps.
The dumps are
referred to toxicity category IV, they
belong to the high and medium pollution rate by the summary parameter of
pollution.
Many useful
elements (Fe, Co, Au, Ag and others) occur in the technogenic dumps that have
been formed by the present time. These elements are of industrial interest for
the retreatment of the mine production wastes.
The studies [3]
state that the iron content in the dumps goes up to 22% and the use of this raw
material is efficient enough and can be compared to the iron ore processing at
the productive mines by its economic parameters.
Cobalt from mine
dumps is of industrial significance and should be a subject to systematic
scientific studies to develop contemporary techniques of waste treatment in
order to obtain the sulphide concentrate for a metallurgical extraction. The
experimental floatation concentration of debris at the Irbinsky mine enabled to
obtain the pyrite concentrate where copper, cobalt and zinc content was up to 6.7
%; 0.42 % and 0.55 % yielding 87,0;
52,0 and 63,6 % correspondingly.
More than 30 mln.
t. of tails presented by a fine material (-2,0 + 0,045 mm) are concentrated at
the dumps of the Mundibashskaya mine. The precious metals gold and silver in
tailings are of the greatest interest. Their content in core samples varies: Au
= 0,1-1,2 (average weighted 0,616) g/t, Ag = 0,5-7,0 g/t. Gold can be
economically extracted with the use of contemporary processing techniques and
first of all the technique of gravity
separation with the use of concentrating table and centrifugal separators. With
the use of centrifugal separation the maximal gold extraction made up 93% with
the gold concentration rate from 8 to 23 units (depending on the head grade of
gold in a sample).
Thus the conclusion
about the great significance of technogenic formations of the Siberian mine
complex and the possibilities of production of valuable, rare and precious metals
as well as construction materials for the Russian industry can be made.
The industrial
significance of dumps retreatment should also consider the ecological component
– the preventable damage to the environment caused by discharges and exhausts
of harmful components and compounds into the water basins and atmosphere. An
important economic and social aspect for towns and settlements is the recovery
of recultivated landscapes particularly in black soil and recreation areas.
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.
Medvedeva N.P., Filippov P.A. On timeliness of technogenic raw materials processing. Materiály VIII
mezinárodní vědecko - praktická conference «Vědecký
pokrok na přelomu tysyachalety - 2012». - Díl 25. Ekologie.
Zeměpis a geologie: Praha. Publishing House «Education and Science». – pp. 45-47.
3.
P.A. Filippov, S.A. Neverov, A.A. Neverov. Technogenic Iron Ore Formations in Siberia as a Secondary Resource
for Production of Ferrous, Rare, Non-Ferrous and Noble Metals // International
Symposium. «Orebody Modelling and Strategic Mine Planning: Old and new
dimensions in a changing world» - Australia, Perth, The Australian
Institute of Mining and Metallurgy.-2009. - pp. 131-135.