Sulfide mining wastes, as well as the natural geochemical anomalies, represent an uncontrolled sources of heavy metals into the environment. As a result of a complex multifactorial process of chemical and biochemical weathering of ore minerals in these landscapes there is a formation of aggressive sulfuric acid solution (upto pH <1) promoting the mobilization of Fe, Cu, Zn and other elements [Nordstrom, 1991]. During the last decade a large number of works cover the development of geotechnical methods of migratory flows management in the fields of waste storing on the basis of experimental studies of the interaction of sulfide minerals with the components of the environment [Alekhin ,et al., 2006]. It is known that the processes of chemical weathering with atmospheric oxygen are limited by the activation phase О2 (Е = + 1.23 В) and noticeably accelerated in the presence of catalysts, whose role in the oxidative horizon of sulphide dumps along with ions, Fe, Cu is acted by nitrogen oxycompounds coming from atmosphere in the form of acid deposition (dry and wet) [Ptitsyn, et al., 2009]. From the point of view of thermodynamics, nitric oxides and products of their interaction with water have higher oxidation potential (Е = + 0.85 + 1.77 В) than univalent copper ions (Е = 0.15 В) and ferric (Е = + 0.77 В). The mechanism of catalysis is extremely complex and currently do not have details. During oxidation in the system there is a number of nitrogen compounds (NO, N2O3, NO2, N2O4, HNO2, NO2, HNO3, NO3, NO, NO2 etc.) with different catalytic activity and varying concentrations. According to numerous experimental studies kinetically most chemically responsive form is the nitrous acid and its dissociation products. At low concentrations (< 0.1 M) the activating effect of HNO2 exceeds the catalytic activity of all other nitrogen oxycompounds by several times. The complete opening of sulfides does not require significant amounts of activator, because the escaping nitric oxides are easily oxidized in the presence of oxygen, and again form nitric acid.
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