Abstract

The aim of this study was to evaluate the feasibility of (bio)hydrometallurgical methods for metal extraction from historical copper slags. Two types of slags (amorphous slag—AS, and crystalline slag—CS) were subjected to 24 to 48 h of leaching with: (i) Sulfuric acid at 0.1, 0.5, and 1 M concentrations at 1%, 5%, and 10% pulp densities (PDs); and (ii) normality equivalent (2 N) acids (sulfuric, hydrochloric, nitric, citric, and oxalic) at pulp densities ranging from 1% to 2%. Bioleaching experiments were performed within 21 days with Acidithiobacillus thiooxidans accompanied by an abiotic control (sterile growth medium). The results demonstrated that the most efficient treatment for amorphous and crystalline slag was bioleaching at 1% PD over 21 days, which led to extraction of Cu at rates of 98.7% and 52.1% for AS and CS, respectively. Among the chemical agents, hydrochloric acid was the most efficient and enabled 30.5% of Cu to be extracted from CS (1% PD, 48 h) and 98.8% of Cu to be extracted from AS (1% PD, 24 h). Slag residues after leaching were characterized by strong alteration features demonstrated by the complete dissolution of fayalite in the case of CS and the transformation of AS to amorphous silica and secondary gypsum. Based on this study, we conclude that amorphous slag is a more suitable candidate for potential metal recovery because of its generally high susceptibility to leaching and due to the generation of residue significantly depleted in metals as the end product. The inventory of economically relevant metals showed that 1 ton of historical copper slag contains metals valued at $47 and $135 for crystalline and amorphous slag, respectively, suggesting that secondary processing of such materials can potentially be both economically and environmentally viable.

Highlights

  • Pyrometallurgical processes involve the generation of various by-products, such as slags, sludges, ashes, and other solid residues [1]

  • The metallurgical slags chosen for this study were: (i) Crystalline fayalite-bearing slag (CS) and (ii) amorphous slag (AS), both resulting from former copper production

  • Environmental impact high short low long comparable high low Metallurgical slags are susceptible to dissolution in inorganic and organic solutions; these wastes should be considered as prospective candidates for metal extraction and recovery processes rather than being disposed of and forgotten

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Summary

Introduction

Pyrometallurgical processes involve the generation of various by-products, such as slags, sludges, ashes, and other solid residues [1]. The slags produced are substantial in volume, for example, every ton of copper produced result in the generation of a double volume equivalent of slag material [2]. Some studies have pointed out that improper slag disposal may cause serious ecological problems. The study of Kasemodel et al (2019) reveals that during transportation of slags from the smelter to the disposal site, a dirt road was heavily contaminated by slag fragments [4]. The authors conclude that high metal content in the dirt road constitutes a serious risk for the nearby population because the material is aerated and transported on the wind, and can be absorbed through inhalation [4]. Another study of Forghani et al (2018) aimed at human risk assessment in southeastern

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