Abstract

The paper presents and discusses experimental data regarding the effect of natural organic matter (e.g. humic acid) on the formation and solubility of secondary solid phases of polyvalent metal ions (e.g. M(VI), M(IV), M(III)) in aqueous solutions of 0.1 M NaClO4 and under normal atmospheric conditions. The experimental work has been carried out using hexavalent uranium as analogue for M(VI), tetravalent thorium, cerium and zirconium as analogues for M(IV) and trivalent samarium and neodymium as analogues for M(III). The solid phases under investigation have been prepared by alkaline precipitation in the presence and absence of humic acid and characterized by TGA, ATR-FTIR, XRD and solubility measurements. The experimental data obtained indicate generally that the solid phases, which are formed in the absence of humic acid, are stable and remain the solubility limiting solid phases even in the presence of increased humic acid concentration (up to 0.5 g l-1) in solution. Although polyvalent metal ions form very stable complex with humic acid, upon base addition in the M(z)-humic acid system decomplexation of the previously formed M(z)-humate complexes and precipitation of two distinct phases occurs, namely, the inorganic and the organic phase. The latter is adsorbed on the particle surface of the former. However, natural organic matter (humic acid) affects the particle size of the solid phases and may lead to reduction of redox-sensitive species. Generally, increasing humic acid concentration results in decreasing crystallite size of the inorganic solid phase. The extent of the effect depends inversely on the solid phase stability.

Highlights

  • The long-term performance assessment for the safe disposal oftoxic elements in underground geological formations requires mechanistic knowledge of the chemical behaviour of the metal ions in aquatic systems, because usually only through underground aquifers migration and dispersion of thetoxic elements in the environment is possible [1]

  • The paper presents and discusses experimental data regarding the effect of natural organic matter on the formation and solubility of secondary solid phases of polyvalent metal ions (e.g. M(VI), M(IV), M(III)) in aqueous solutions of 0.1 M NaClO4 and under normal atmospheric conditions

  • In this paper we present and discuss experimental data from studies regarding the effect of natural organic matter (NOM) and humic acid on the solid phase formation of polyvalent metal ions in aqueous solutions

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Summary

Introduction

The long-term performance assessment for the safe disposal of (radio)toxic elements (e.g. heavy metal ions) in underground geological formations (e.g. clay formations, granite, etc.) requires mechanistic knowledge of the chemical behaviour of the metal ions in aquatic systems, because usually only through underground aquifers migration and dispersion of the (radio)toxic elements in the environment is possible [1]. Actinides and lanthanides show usually similar chemical behaviour in solid and aqueous phase, if present in the same oxidation state [2]. The chemical behaviour of polyvalent metal ions in natural systems is governed by hydrolysis, complexation with naturally occuring ligands, colloid generation, interaction with mineral surfaces and solid phase formation [1]. The investigation of formed solid phases is of particular interest because secondary phases may represent important sinks for (radio)toxic metal ions within nuclear spent fuel and (radio)toxic waste repositories and determine their solubility and mobility in the geosphere. Investigations on the impact of NOM on solid phase formation and stability are of fundamental importance because NOM (here represented by humic acid) is omnipresent in natural waters and may affect the solution chemistry of metal ions (e.g. complex and colloid formation). In vivo and in vitro studies clearly show, that organic matter strongly affects crystal growth as well as texture of minerals and inorganic solids [8,9,10,11,12,13,14,15]

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