Leaching experiments revealed high mobility of nickel from ferronickel slag in seawater, highlighting risks in disposal methods.
This study investigates the environmental stability of ferronickel slag (FNS) and primary lead slags (GCS and FCS) from historical metallurgical complexes in Greece, in rainwater and seawater media. Leaching experiments revealed that nickel is the most mobile element from FNS (43.5 μg·g−1 in seawater after 90 days). Chromium release, on the other hand, is very limited, not exceeding 0.04 μg·g−1. In lead slags, zinc and lead exhibit significant leaching (up to 650 and 230 μg·g−1, respectively), while arsenic release reaches 22.6 μg·g−1. GCS contains pores primarily in the range of 50–90 Å. The majority of pore volume in FCS is centered around 30 Å. The porosity appears to have a significant effect on the element’s leachability. Pb, Zn, As, Sb, and Cd are released in significantly higher amounts from the finely porous FCS compared to GCS. Thermodynamic modeling was used to identify the pollutant speciation in water media in relation to the oxygen concentration. The release of toxic elements such as Cr from FNS and As from lead slags is enhanced under oxic (open-air) conditions. Therefore, their land disposal poses a greater environmental threat compared to sea disposal, where anoxic conditions prevail.
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Samouhos et al. (2025) studied this question.
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