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The main subject of this study is fly ash created during coal combustion in Rybnik Power Station in Upper Silesia in the southern part of Poland. This is the biggest block power station in this region. Gener­ated power is 1600 MW. Annual dust emission from professional energy in Upper Silesia is estimated at 32.8 thousand tons, which is about 22% of total national emissions. X-ray powder diffraction, Analytic Scanning Electron Microscopy (ASEM) and Induced Couple Mass Spectrometry (ICP- MS) methods have been applied extensively to heavy metals (Cu, Ni, Pb, Zn, Cr, Cd) content analysis and their host mineral phases identification. Concentrations of Cu, Ni, Pb, Zn, Cr and Cd as well as mineral composition of fly ash being their carriers have been specified. Average Zn concentrations in fly ash are 120 ppm, but for all other elements the averege concentrations were 38 ppm for Cu, 41 ppm for Ni, 44 ppm for Pb, 64 ppm for Cr and 3 ppm for Cd. Amorphic aluminosilicate substances, oxides and sulphides are mineral phases containing heavy metals. The sizes of these particles are up to 12 |im.
The aim of this work was to present the mineral composition of ashes which were the result of burning coal in individual home furnaces in the area of Piekary Śląskie. Ashes samples were examined by X-ray powder diffraction and analytical scanning electron microscopy. Main components of the ash particles is aluminosilicate glaze containing such elements as iron, calcium, sodium, potassium, copper, lead, nickel, phosphorus, titanium, barium and sulphur. Solid waste as ashes, which were the result of the process of burning coal in individual home furnaces can be characterized by the majority of particles of the size not larger than several micrometers. These particles have mostly irregular or spherical shapes. The knowledge of phase composition of the examined waste has a great significance while estimating their influence on environment, especially when considering storage of ashes with community waste.
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