Abstract

The zinc content of basic oxygen furnace (BOF) sludges is too high for direct recycling into the blast furnace via the sinter plant, as excessive zinc concentrations are detrimental for the refractory lining of the blast furnace. However, by partial and selective removal of zinc from the BOF sludge, the residual sludge can be used as a secondary iron resource in the blast furnace. In this paper, BOF sludge was leached with aqueous ammonia, aqueous solutions of ammonium salts (chloride, carbonate, and sulfate), and aqueous mixtures of ammonia and ammonium salt. The mixtures of ammonia and ammonium salt could leach more zinc with respect to either the aqueous ammonia or the aqueous ammonium salt solution. The ammonia–ammonium carbonate (AAC) mixture was selected as the most suitable lixiviant due to the high zinc leaching efficiency in combination with a high selectivity towards iron; furthermore, this combination does not introduce unwanted chloride or sulfate impurities in the residue. The leaching process was optimized in terms of the liquid-to-solid ratio, total ammonia concentration, ammonium:ammonia molar ratio, temperature, and leaching time. The co-dissolved iron was precipitated as a hydroxide after oxidation of ferrous to ferric ions by an air stream, without co-precipitation of zinc, while the dissolved zinc could be easily recovered as zinc sulfide by precipitation with ammonium sulfide. The (almost) closed-loop process was successfully up-scaled from 10 mL to 1 L scale.Graphical

Highlights

  • The average generation of basic oxygen furnace (BOF) dusts and sludges is approximately 22 kg/tonne of crude steel, with a minimum of 10 kg/tonne of crude steel and a Journal of Sustainable Metallurgy (2020) 6:680–690 maximum of 40 kg/tonne of crude steel [1]

  • The BOF sludges used in this work were collected before the filter press

  • Two samples of BOF sludge were used in this work, namely BOF1 and BOF2

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Summary

Introduction

The average generation of basic oxygen furnace (BOF) dusts and sludges is approximately 22 kg/tonne of crude steel, with a minimum of 10 kg/tonne of crude steel and a Journal of Sustainable Metallurgy (2020) 6:680–690 maximum of 40 kg/tonne of crude steel [1]. Due to improvements in the gas cleaning systems, more material is being collected rather than exiting into the atmosphere via exhaust stacks This leads to slightly increasing production rates of BOF dusts and sludges over the years. The primary dust contains such a low zinc content, but rich in iron, that it has a good quality compared to virgin iron ores. It can be used as a secondary iron resource [2]. The zinc distribution and zinc speciation in a zinc-rich (3.4% ZnO) BOF sludge by micro-XRD and micro-XANES highlighted that the main zinc phases were franklinite (­ ZnFe2O4) and smithsonite (­ ZnCO3) [5, 6]. The composition and phase distribution of BOF sludges are showing a large variability, depending on the production plant and specific campaigns

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