Abstract

The paper presents the results of heavy metals mobility obtained by sequential extraction method and leaching test. Heavy metals in solid waste material occur in different forms and phases that differ in terms of the toxicity, mobility and bioavailability. The sequential extraction analysis is widely used in order to predict the behaviour of heavy metals in a solid material. The sequential extraction methods involve a gradual separation of metals in various forms by means of specific extractants. The material used in the research applied bottom ash derived from households. The results of heavy metals concentrations (Cd, Pb, Ni, Cr, Cu, Zn) in extractable forms and total content in waste were presented. The five forms of heavy metals were determined. The concentrations of heavy metals were analyzed by FAAS. The lowest concentrations of analyzed heavy metals were determined in the exchangeable form. The author observed that the particular elements occurred mainly in forms: zinc and cadmium associated with carbonates, lead and copper in the organic and residual form, chromium and nickel in the residual form. Heavy metals in the residual fraction do not pose a possible environment hazard. The application of speciation analysis of heavy metals in bottom ash provide the means to assess the content of dissoluble forms of metals in water relative to their total content. This information is useful in assessing the migration capabilities of heavy metal ions from waste to the ground-water environment. The potential for the reuse of bottom ash was also discussed in the paper.

Highlights

  • Combustion of fuels in households is accompanied by the production of bottom ashes

  • Immobile associations were the dominant fractions for lead, nickel and chromium, and they were mainly found to be bound to aluminosilicates forming residual fraction (F5)

  • Heavy metals were characterized by low mobility in the eluates derived from ashes in accordance with PN-EN 12457-2 standard

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Summary

Introduction

Combustion of fuels in households is accompanied by the production of bottom ashes. They form the by-product of the combustion of hard coal, coke, eco-pea coal or wood in boilers in household heating systems. The most common way of utilizing household ash was based on depositing it in landfills As a result of applying sequential analysis tools, it is possible to determine the concentrations of given elements in a sludge – soil – plant – human food chain [4]. This is very important aspects for the case when waste is designed for use in agriculture

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