Biological Sciences
/ 6. Microbiology
Ph D in biology Berseneva O.A
Irkutsk State University, Russia
Innovations
and new resource-saving technologies in the processing of sulphide ore
Currently,
in connection with one of the global environmental problems of modernity
(mineral depletion of natural resources) especially important is search and
development of resource-saving technologies. One of the approaches
to solving problem of depletion of mineral raw
materials is the use bioleaching
based în the extraction of chemicals
compounds from multicomponent microorganisms through their dissolution in
aqueous medium with bacteria or their metabolites [1,3]. Thanks to the
technology of bacterial leaching it is
possible extraction from ores, mining waste and metallurgical production of
valuable components (different metals) [2,4,5].
Useful for bacterial leaching of
mineral products has properties of about 30 bacterial cultures [2,7,8,9,10]. However, the main actively applied in practice, bacterial
leaching of metals is the kind thiobacteria named Thiobacillus ferrooxidans. [2,7].
This type of bacteria is capable of oxidizing practically all metal sulfides [2,7].
The aim of this study was isolation of autochthonous
acidophilic chemolithotrophic microorganisms associations for further possible
application of these associations in the technology of bacterial leaching
technology of sulfide ores from waste.
Sources for the isolation of microorganisms were coal
dumps in the area is actively developing coal deposits "Cheremhovsky"
(Irkutsk region, Cheremhovo).
Getting funded cultural association chemolithotrophic autochthonous
microorganisms from the oxidized ore coal mine "Cheremhovsky" was
carried out in mesophilic conditions (30 ± 20 ° C) with a solution of mineral
salts of Silverman-Lyundgrena and Waxman.
For the cultivation of microorganisms of 1 g of ore was thoroughly
stirred in 100 ml distilled water and added to 1 ml of suspension in each flask
with selection medium. As a control we used sterile selection medium without
sample.
Determination of the amount of iron (II) was carried out
photometrically. For this took 1 ml of culture liquid with cells are placed in
a test tube was added 2 ml of 10% sulfosalicylic acid; 0.1 ml of 2N sulfuric
acid, stirred and the solution volume was adjusted to 10 ml with distilled
water. The absorbance of the mixture was
measured with a spectrophotometer NanoPhotometer P 330, Implen at 510 nm.
cuvette width of 10 mm. Determination led by the values of the standard curve,
which was built in the same conditions, using a sample of iron-ammonium alum
with 0.1-1 mg / ml iron (II) solution. The duration of the process was 30 days [6].
In the process of accumulation of microbial cultures,
within a month of cultivation of the investigated samples of coal ore mine
"Cheremhovsky " highlighted various representatives of microbial
associations.
The study microbial associations is presented species A. ferroxidans (motile, gram-negative,
single and in chains asporogenous rods, aerobic, moderate thermophiles (upper
temperature limit of 400C ), pH tolerance range of 2.0 to 4.0 ) and A. thiooxidans ( mobile, gram-negative,
small nonsporogenous sticks, aerobic, mesophiles (optimum temperature of 30 -
370C) , the optimum development pH 2,0-4,0.
Studying the dynamics of substrate oxidation revealed that increasing
the concentration of iron in solution starting from the 4 th to 15 th day of
cultivation, and increases from an initial concentration of 1 g/l at 15 day in medium Silverman 7 times, and in medium Waksman 5
times îò day 8 day of cultivation.
The results of these studies have shown that
the highest oxidized ability found in medium
Silverman-Lundgrena, but the allocation of iron affects more time than medium
Waksman.
Therefore, we assume that data obtained to determine
the living condition of the chemolithotrophic microbial associations
and intensity of the oxidation of iron can be used to extraction of iron from
sulfide ores.
References
1. Acid mine drainage biogeochemistry at Iron Mountain, California. / G.
K. Druschel, B. J. Baker, T. M. Gihring, J. F. Banfield // Geochemical transactions.
– 2004. – Vol. 5. – ¹. 2. – P. 13–32.
2. Biotechnology metal / G.I. Karovayko
[et al.]. – M.:
Center for International Projects GKNT, 1989. –
P.375.
3.
Biochemistry of bacterial
leaching – direct vs. indirect bioleaching.
/ W. Sand, T. Gehrke, P.G. Jozsa, A. Schippers // Hydrometallurgy. – 2001. – Vol. 59. – P. 159-175.
4. Berseneva OA
Bacterial-chemical oxidation of metals (leaching) environmentally friendly
future industry / OA Berseneva // monthly scientific journal "Eurasian
Union of Scientists ¹4 (Part 3), 2015. – 26 ð.
5. Berseneva OA
Eco-friendly technology to extract metals from sulphide ores / OA Berseneva //
XIII International scientific-technical conference "Modern problems of
ecology", Tula, 2015, P. 10-11.
6. Chakchir B.A. Photometric methods of analysis / B.A. Chakchir, G.M. Alekseeva:
Guidelines. – SPb.: Publishing house SPHFA,
2002. – 44 p.
7. Devasia P. Bacterial leaching. Biotechnology in the mining industry. /
P. Devasia, K. A. Natarajan // Resonance. – 2004. – Vol. 9. – P. 27–34.
8. Rawlings D. E. Characteristics and adaptability of iron- and
sulfuroxidizing microorganisms used for the recovery
of metals from minerals and their concentrates. / D. E. Rawlings // Microbial
cell factories. – 2005. – Vol. 4. – No. 13. – P. 1–15.
9. Rawlings D. E. Heavy metal mining using microbes. /
D. E. Rawlings // Annual review of microbiology. – 2002. – Vol. 56. – P. 65–91.
10.
Schippers A. Microorganisms
involved in bioleaching and nucleic acid-based molecular methods for their
identification and quantification.
Chapter 1. / A. Schippers //
Microbial processing of metal sulfides. Springer Netherlands. – 2007. – P.
3–33.